You're using an outdated browser. This website will not display correctly and some features will not work.
Learn more about the browsers we support for a faster and safer online experience.

 

Environmental Protection Act
Loi sur la protection de l’environnement

R.R.O. 1990, REGULATION 347

Amended to O. Reg. 461/05

GENERAL — WASTE MANAGEMENT

Historical version for the period August 10, 2005 to March 30, 2006.

This Regulation is made in English only.

Skip Table of Contents

CONTENTS

 

 

Sections

 

Definitions

1

 

Designation and Exemption of Wastes

2-3

 

Classification and Exemption of Waste Disposal Sites

4-6

 

Classification and Exemption of Waste Management Systems

7-10

 

Standards for Waste Disposal Sites

11-15

 

Standards for Waste Management Systems

16-16.1

 

Management of Asbestos Waste

17

 

Waste Generation Facilities

17.1-17.2

 

Generator Registration

18

 

Manifests — Generator Requirements

19

 

Manifests — Carrier Requirements

20-22

 

Manifests — Transport within Ontario

23

 

Manifests — Transport out of Ontario

24

 

Manifests — Transport into Ontario

25

 

Manifests — Transport through Ontario

26

 

Refusals

27

 

On-Site Incinerators

28

 

Woodwaste Combustor Sites

28.1-28.2

 

Waste-Derived Fuel Sites

28.3-28.5

 

Existing Hospital Incinerators

29

 

Stationary Refrigerant Waste

30-35

 

Mobile Refrigerant Waste

36-42

 

Selected Waste Depots

42.1-60

 

Pesticide Container Depots

61-73

 

Land Disposal of Hazardous Waste

74-85

Schedule 1

Hazardous industrial wastes

 

Schedule 1

Hazardous industrial waste

 

Schedule 1.1

Exempt hazardous industrial wastes

 

Schedule 1.1

Exempt hazardous industrial wastes

 

Schedule 2

Part a — acute hazardous waste chemicals

 

Schedule 2

Part b — hazardous waste chemicals

 

Schedule 2

Part a — acute hazardous waste chemical

 

Schedule 2

Part b — hazardous waste chemical

 

Schedule 2.1

Exempt acute hazardous waste chemicals

 

Schedule 2.2

Exempt hazardous waste chemicals

 

Schedule 3

Severely toxic contaminants

 

Schedule 3

Severely toxic contaminants

 

Schedule 4

Leachate quality criteria

 

Schedule 4

Leachate quality criteria

 

Schedule 5

Test method for the determination of “liquid waste” (slump test)*

 

Schedule 5

Land disposal requirements for characteristic wastes

 

Schedule 6

Universal treatment standards (uts) for characteristic wastes

 

Schedule 7

Treatment methods and standards

 

Schedule 8

Alternative treatment for hazardous debris

 

Schedule 10

 

 

Schedule 11

 

 

Schedule 12

 

 

Schedule 13

 

 

Definitions

1. (1) In this Regulation,

“access road” means a road that leads from a public road to a waste disposal site;

“acute hazardous waste chemical” means,

(a) a commercial waste chemical having a generic name listed in Part A of Schedule 2, other than a waste described in Schedule 2.1,

Note:  On January 1, 2007, clause (a) is revoked and the following substituted:

(a) a commercial waste chemical listed as an acute hazardous waste chemical in Part A of Schedule 2, other than a waste described in Schedule 2.1,

See:  O. Reg. 461/05, ss. 1 (1), 29 (3).

(b) a mixture of a waste referred to in clause (a) and any other waste or material, or

(c) a waste derived from a waste referred to in clause (a), unless,

(i) the waste that is derived from the waste referred to in clause (a) is listed in Schedule 2.1, or

(ii) the waste that is derived from the waste referred to in clause (a) is produced in accordance with a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of the acute hazardous waste chemical from which it was derived;

“agricultural waste” means waste, other than sewage, resulting from farm operations, including animal husbandry and where a farm operation is carried on in respect of food packing, food preserving, animal slaughtering or meat packing, includes the waste from such operations;

Note:  On January 1, 2007, subsection (1) is amended by adding the following definition:

“aqueous waste” means waste that is aqueous and contains less than 1 per cent total organic carbon by weight and less than 1 per cent total suspended solids by weight;

See:  O. Reg. 461/05, ss. 1 (2), 29 (3).

“asbestos waste” means solid or liquid waste that results from the removal of asbestos-containing construction or insulation materials or the manufacture of asbestos-containing products and contains asbestos in more than a trivial amount or proportion;

“carrier” means the operator of a waste transportation system;

“cell”, in respect of a landfilling site, means a deposit of waste that has been sealed by cover material so that no waste deposited in the cell is exposed to the atmosphere;

“characteristic waste” means hazardous waste that is,

(a) corrosive waste,

(b) ignitable waste,

(c) leachate toxic waste, or

(d) reactive waste;

“commercial waste” includes asbestos waste;

“commercial waste chemical” means a waste that is or contains a commercial chemical product or manufacturing chemical intermediate of a specified generic name and includes,

(a) an off-specification commercial chemical product or manufacturing chemical intermediate which, if it met specifications, would have the specified generic name,

(b) residues or contaminated material from the clean-up of a spill of a commercial chemical product or manufacturing chemical intermediate of the specified generic name or of an off-specification commercial chemical product or manufacturing chemical intermediate which, if it met specifications, would have the specified generic name, or

(c) an empty container or the liner from an empty container that contained a commercial chemical product or manufacturing chemical intermediate of the specified generic name, or an off-specification commercial chemical product or manufacturing chemical intermediate which, if it met specifications, would have the specified generic name, or residues or contaminated materials from the clean-up of a spill of any of them, unless the empty container or the liner from the empty container has been triple rinsed,

but, except as specified in clause (a), (b) or (c), does not include a waste stream or waste material contaminated with material of the specified generic name;

“composting” means the treatment of waste by aerobic decomposition of organic matter by bacterial action for the production of stabilized humus;

“corrosive waste” means a waste that,

(a) is aqueous and has a pH less than or equal to two or greater than or equal to 12.5 as determined by a pH meter,

(b) is a liquid and corrodes steel (SAE 1020) at a rate greater than 6.35 millimetres per year at a test temperature of 55° Celsius using test NACE TM-01-69 or an equivalent test approved by the Director, or

(c) is a solid and, when prepared in a mixture or solution with distilled water that is 50 per cent waste by weight, has a pH less than or equal to two or greater than or equal to 12.5 as determined by a pH meter;

“cover material” means soil or other material approved for use in sealing cells in landfilling;

“dead animal” means an animal that dies naturally or from disease or by reason of accident and includes parts thereof;

“derelict motor vehicle” means a motor vehicle that,

(a) is inoperable, and

(b) has no market value as a means of transportation, or, has a market value as a means of transportation that is less than the cost of repairs required to put it into operable condition;

“Director” means the Director of the Waste Management Policy Branch of the Ministry and includes an alternate named by him or her;

“domestic waste” includes asbestos waste;

“dump” means a waste disposal site where waste is deposited without cover material being applied at regular intervals;

“dust suppressant” means a waste used for dust suppression in accordance with a certificate of approval or provisional certificate of approval for a dust suppression waste management system;

“dust suppression site” means a waste disposal site where dust suppressant is deposited;

“electroplating” includes common and precious metal electroplating, anodizing, chemical etching and milling, and includes cleaning and stripping associated with common and precious metal electroplating, anodizing, chemical etching and milling, but does not include chromating, phosphating, immersion plating, colouring or other chemical conversion coating, electroless plating or printed circuit board manufacturing;

“empty container” means a container from which all wastes and other materials have been removed using the removal practices such as pumping or pouring commonly used for the specific materials and that contains less than 2.5 centimetres of material on the bottom of the container;

“existing hospital incinerator” means an incinerator put into operation before the 31st day of December, 1985 owned by a hospital within the meaning of the Public Hospitals Act at which pathological waste but no hauled liquid industrial waste or other hazardous waste is incinerated;

“fly-ash” means particulate matter removed from combustion flue gases;

“generator” means the operator of a waste generation facility;

“grinding” means the treatment of waste by uniformly reducing the waste to particles of controlled maximum size;

“hauled liquid and hazardous waste collection system” means a waste management system or any part thereof for the collection, handling, transportation, storage or processing of hauled liquid industrial waste or hazardous waste but does not include the disposal thereof;

“hauled liquid industrial waste” means liquid industrial waste transported in a tank or other container for treatment or disposal;

“hauled sewage” means,

(a) domestic waste that is human body waste, toilet or other bathroom waste, waste from other showers or tubs, liquid or water borne culinary or sink waste or laundry waste, and

(b) other waste that is suitable for storage, treatment or disposal in a sewage system regulated under Part 8 of the building code made under the Building Code Act, 1992, if the waste is not fully disposed of at the site where it is produced, other than,

(i) waste from a sewage works approved under section 53 of the Ontario Water Resources Act that is conveyed away from the site where it is produced by a sewer approved under that section, or

(ii) waste in a vehicle sewage holding tank;

“hazardous industrial waste” means,

(a) a generic or specific waste listed in Schedule 1, other than a waste described in Schedule 1.1,

Note:  On January 1, 2007, clause (a) is revoked and the following substituted:

(a) a waste listed as a hazardous industrial waste in Schedule 1, other than a waste described in Schedule 1.1,

See:  O. Reg. 461/05, ss. 1 (6), 29 (3).

(b) a mixture of a waste referred to in clause (a) and any other waste or material, or

(c) a waste derived from a waste referred to in clause (a), unless,

(i) the waste that is derived from the waste referred to in clause (a) is listed in Schedule 1.1, or

(ii) the waste that is derived from the waste referred to in clause (a) is produced in accordance with a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of the hazardous industrial waste from which it was derived;

“hazardous waste” means a waste that is a,

(a) hazardous industrial waste,

(b) acute hazardous waste chemical,

(c) hazardous waste chemical,

(d) severely toxic waste,

(e) ignitable waste,

(f) corrosive waste,

(g) reactive waste,

(h) radioactive waste, except radioisotope wastes disposed of in a landfilling site in accordance with the written instructions of the Canadian Nuclear Safety Commission,

(i) pathological waste,

(j) leachate toxic waste, or

(k) PCB waste,

but does not include,

(l) hauled sewage,

(m) waste from the operation of a sewage works subject to the Ontario Water Resources Act where the works,

(i) is owned by a municipality,

(ii) is owned by the Crown or the Ontario Clean Water Agency, subject to an agreement with a municipality under the Ontario Water Resources Act, or

(iii) receives only waste similar in character to the domestic sewage from a household,

(n) domestic waste,

(o) incinerator ash resulting from the incineration of waste that is neither hazardous waste nor liquid industrial waste,

(p) waste that is a hazardous industrial waste, hazardous waste chemical, ignitable waste, corrosive waste, leachate toxic waste or reactive waste and that is produced in any month in an amount less than five kilograms or otherwise accumulated in an amount less than five kilograms,

(q) waste that is an acute hazardous waste chemical and that is produced in any month in an amount less than one kilogram or otherwise accumulated in an amount less than one kilogram,

(r) an empty container or the liner from an empty container that contained hazardous industrial waste, hazardous waste chemical, ignitable waste, corrosive waste, leachate toxic waste or reactive waste,

(s) an empty container of less than twenty litres capacity or one or more liners weighing, in total, less than ten kilograms from empty containers, that contained acute hazardous waste chemical,

(t) the residues or contaminated materials from the clean-up of a spill of less than five kilograms of waste that is a hazardous industrial waste, hazardous waste chemical, ignitable waste, corrosive waste, leachate toxic waste or reactive waste, or

(u) the residues or contaminated materials from the clean-up of a spill of less than one kilogram of waste that is an acute hazardous waste chemical;

“hazardous waste chemical” means,

(a) a commercial waste chemical having a generic name listed in Part B of Schedule 2, other than a waste described in Schedule 2.2,

Note:  On January 1, 2007, clause (a) is revoked and the following substituted:

(a) a commercial waste chemical listed as a hazardous waste chemical in Part B of Schedule 2, other than a waste described in Schedule 2.2,

See:  O. Reg. 461/05, ss. 1 (10), 29 (3).

(b) a mixture of a waste referred to in clause (a) and any other waste or material, or

(c) a waste derived from a waste referred to in clause (a), unless,

(i) the waste that is derived from the waste referred to in clause (a) is listed in Schedule 2.2, or

(ii) the waste that is derived from the waste referred to in clause (a) is produced in accordance with a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of the hazardous waste chemical from which it was derived;

“hospital incinerator” means an incinerator owned by a hospital within the meaning of the Public Hospitals Act;

“ignitable waste” means a waste that,

(a) is a liquid, other than an aqueous solution containing less than 24 per cent alcohol by volume and has a flash point less than 61° Celsius, as determined by the Tag Closed Cup Tester (ASTM D-56-79), the Setaflash Closed Cup Tester (ASTM D-3243-77 or ASTM D-3278-78), the Pensky-Martens Closed Cup Tester (ASTM D-93-79), or as determined by an equivalent test method approved by the Director,

(b) is a solid and is capable, under standard temperature and pressure, of causing fire through friction, absorption of moisture or spontaneous chemical changes and, when ignited, burns so vigorously and persistently that it creates a danger,

(c) is an ignitable compressed gas (Class 2, Division 1) as defined in the regulations under the Transportation of Dangerous Goods Act (Canada), or

(d) is an oxidizing substance (Class 5, Divisions 1 and 2) as defined in the regulations under the Transportation of Dangerous Goods Act (Canada);

“incinerator ash” means the ash residue, other than fly-ash, resulting from incineration where the waste is reduced to ashes containing by weight less than 10 per cent of combustible materials;

“incinerator waste” means the residue from incineration, other than incinerator ash and fly-ash;

“individual collection system” means the collection of a householder’s own domestic wastes by a householder and the transportation of such wastes to a waste disposal site by the householder;

“industrial waste” means waste from,

(a) an enterprise or activity involving warehousing, storage or industrial, manufacturing or commercial processes or operations,

(b) research or an experimental enterprise or activity,

(c) an enterprise or activity to which clause (a) would apply if the enterprise or activity were carried on for profit,

(d) clinics that provide medical diagnosis or treatment, or

(e) schools, laboratories or hospitals;

“inert fill” means earth or rock fill or waste of a similar nature that contains no putrescible materials or soluble or decomposable chemical substances;

“intact manifest” means a paper manifest as provided by the Ministry, with all six parts intact;

“in-vehicle sewage” means waste produced in a vehicle that is human body waste, toilet or other bathroom waste, waste from other showers or tubs, liquid or water borne culinary or sink waste, laundry waste or similar waste that would normally be carried away by a sewer if it were not produced in a vehicle;

“land disposal” means, with respect to a waste, the deposit or disposal of the waste upon, into, in or through land, including,

(a) the deposit of the waste at a dump,

(b) the landfilling of the waste,

(c) the discharge of the waste into a geological formation by means of a well, and

(d) the landfarming of the waste, in the case of a petroleum refining waste,

and “land disposed” has a corresponding meaning;

“landfarming” means the biodegradation of petroleum refining wastes by naturally occurring soil bacteria by means of controlled application of the wastes to land followed by periodic tilling;

“landfilling” means the disposal of waste by deposit, under controlled conditions, on land or on land covered by water, and includes compaction of the waste into a cell and covering the waste with cover materials at regular intervals;

“leachate toxic waste” means a waste producing leachate containing any of the contaminants listed in Schedule 4 at a concentration equal to or in excess of the concentration specified for that contaminant in Schedule 4 using the Toxicity Characteristic Leaching Procedure;

“liquid industrial waste” means waste that is both liquid waste and industrial waste but does not include,

(a) hauled sewage,

Note:  On January 1, 2007, clause (a) is revoked and the following substituted:

(a) hazardous waste,

(a.1) hauled sewage,

See:  O. Reg. 461/05, ss. 1 (14), 29 (3).

(b) waste from the operation of a sewage works described in clause (m) of the definition of “hazardous waste”,

(c) waste from the operation of a water works subject to the Ontario Water Resources Act or the Safe Drinking Water Act, 2002,

(d) waste that is produced in any month in an amount less than twenty-five litres or otherwise accumulated in an amount less than twenty-five litres,

(e) waste directly discharged by a generator from a waste generation facility into a sewage works subject to the Ontario Water Resources Act or established before April 3, 1957 or into a sewage system regulated under Part 8 of the building code made under the Building Code Act, 1992,

(f) waste that results directly from food processing and preparation operations, including food packing, food preserving, wine making, cheese making and restaurants,

(g) drilling fluids and produced waters associated with the exploration, development or production of crude oil or natural gas,

(h) processed organic waste, or

(i) asbestos waste;

“listed waste” means hazardous waste that is,

(a) an acute hazardous waste chemical,

(b) hazardous industrial waste,

(c) a hazardous waste chemical, or

(d) severely toxic waste;

“manifest” means a numbered document called a manifest that was obtained from the Ministry and includes a paper or electronic manifest;

“Manual” means the publication entitled “Registration Guidance Manual for Generators of Liquid Industrial and Hazardous Waste”, published by the Ministry of Environment and Energy and dated April 1995, as amended from time to time;

“marine craft waste disposal system” means a waste disposal system operated by a person or a municipality for the receiving of waste from marine craft for deposit in holding tanks;

“Ministry website” means the website at www.ene.gov.on.ca;

“mobile refrigerant waste” means refrigerant removed from the air-conditioning, heat pump, refrigeration or freezer unit of anything used for the purposes of transportation;

“mobile refrigerant waste collector” means a mobile refrigerant waste management system that collects mobile refrigerant waste it has removed from equipment in which refrigerant is used;

“mobile refrigerant waste recycler” means a mobile refrigerant waste management system that receives mobile refrigerant waste from other mobile refrigerant waste management systems and recycles it;

“municipal waste” means,

(a) any waste, whether or not it is owned, controlled or managed by a municipality, except,

(i) hazardous waste,

(ii) liquid industrial waste, or

(iii) gaseous waste, and

(b) solid fuel, whether or not it is waste, that is derived in whole or in part from the waste included in clause (a);

Note:  On January 1, 2007, subsection (1) is amended by adding the following definition:

“non-aqueous waste” means waste that is not aqueous waste;

See:  O. Reg. 461/05, ss. 1 (17), 29 (3).

“non-hazardous solid industrial waste” means industrial waste that is not liquid industrial waste and is not hazardous waste and includes asbestos waste;

“on-site garbage grinder” means a grinder,

(a) used for the treatment of waste that is subsequently discharged as sewage, and

(b) located in a building or structure used principally for functions other than waste management;

“on-site incinerator” means an incinerator located at a site used principally for functions other than waste management in which only waste generated on that site is incinerated;

“on-site road” means a road for the movement of vehicles and equipment within a waste disposal site;

“organic soil conditioning” means the incorporation of processed organic waste in the soil to improve its characteristics for crop or ground cover growth;

“packing and baling” means the treatment of waste by its compression into blocks or bales and binding or sheathing the blocks with wire, metal, plastic or other material;

“pathological waste” means,

(a) any part of the human body, including tissues and bodily fluids, but excluding fluids, extracted teeth, hair, nail clippings and the like, that are not infectious,

(b) any part of the carcass of an animal infected with a communicable disease or suspected by a licensed veterinary practitioner to be infected with a communicable disease,

(c) non-anatomical waste infected with communicable disease,

(d) a mixture of a waste referred to in clause (a), (b) or (c) and any other waste or material, or

(e) a waste derived from a waste referred to in clause (a), (b) or (c), unless the waste that is derived from the waste referred to in clause (a), (b) or (c) is produced in accordance with a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of pathological waste referred to in clause (a), (b) or (c);

“PCB” has the same meaning as in Regulation 362 of the Revised Regulations of Ontario, 1990 (Waste Management — PCBs) made under the Act;

“PCB waste” has the same meaning as in Regulation 362 of the Revised Regulations of Ontario, 1990 (Waste Management — PCBs) made under the Act;

“processed organic waste” means waste that is predominantly organic in composition and has been treated by aerobic or anaerobic digestion, or other means of stabilization, and includes sewage residue from sewage works that are subject to the provisions of the Ontario Water Resources Act;

“radioactive waste” includes,

(a) a mixture of radioactive waste and any other waste or material, and

(b) a waste derived from radioactive waste, unless the waste that is derived from the radioactive waste is produced in accordance with a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of radioactive waste;

“reactive waste” means a waste that,

(a) is normally unstable and readily undergoes violent change without detonating,

(b) reacts violently with water,

(c) forms potentially explosive mixtures with water,

(d) when mixed with water, generates toxic gases, vapours or fumes in a quantity sufficient to present danger to human health or the environment,

(e) is a cyanide or sulphide bearing waste which, when exposed to pH conditions between two and 12.5, can generate toxic gases, vapours or fumes in a quantity sufficient to present danger to human health or the environment,

(f) is capable of detonation or explosive reaction if it is subjected to a strong initiating source or if heated under confinement,

(g) is readily capable of detonation or explosive decomposition or reaction at standard temperature and pressure,

(h) is an explosive (Class 1) as defined in the regulations under the Transportation of Dangerous Goods Act (Canada);

“receiver” means the operator of any facility to which waste is transferred by a carrier;

“Regional Director” means a Director appointed under section 5 of the Act and responsible for a region established by the Ministry for administrative purposes, but does not mean the Director of the Waste Management Policy Branch of the Ministry or an alternate named by him or her;

“scavenging” means the uncontrolled removal of reusable material from waste at a waste disposal site;

“Section 39 Director” means a Director appointed under section 5 of the Act for purposes of section 39 of the Act;

“severely toxic waste” means,

(a) a waste that contains a contaminant listed in Schedule 3 at a concentration greater than one part per million,

Note:  On January 1, 2007, clause (a) is revoked and the following substituted:

(a) a waste that contains a contaminant listed as a severely toxic contaminant in Schedule 3 at a concentration greater than one part per million,

See:  O. Reg. 461/05, ss. 1 (20), 29 (3).

(b) a mixture of a waste referred to in clause (a) and any other waste or material, or

(c) a waste derived from a waste referred to in clause (a), unless the waste that is derived from the waste referred to in clause (a) is produced in accordance with a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of severely toxic waste referred to in clause (a);

“site” means one property and includes nearby properties owned or leased by the same person where passage from one property to another involves crossing, but not travelling along, a public highway;

Note:  On August 31, 2007, subsection (1) is amended by adding the following definition:

“soil mixture” includes a mixture of soil and liquids, sludges or solids, where,

(a) the mixture cannot be separated by simple mechanical removal processes; and

(b) based on visual inspection, the volume of the mixture is made up primarily of soil or other finely divided material that is similar to soil;

See:  O. Reg. 461/05, ss. 1 (21), 29 (4).

“stationary refrigerant waste” means refrigerant that is not mobile refrigerant waste and that is removed from an air-conditioning unit, heat pump, refrigeration or freezer unit;

“stationary refrigerant waste collector” means a stationary refrigerant waste management system that collects stationary refrigerant waste it has removed from equipment in which refrigerant is used;

“stationary refrigerant waste recycler” means a stationary refrigerant waste management system that receives stationary refrigerant waste from other stationary refrigerant waste management systems and recycles it;

“subject waste” means,

(a) liquid industrial waste, and

Note:  On December 31, 2009, clause (a) is revoked and the following substituted:

(a) liquid industrial waste,

See:  O. Reg. 461/05, ss. 1 (22), 29 (5).

(b) hazardous waste,

Note:  On December 31, 2009, clause (b) is revoked and the following substituted:

(b) hazardous waste, and

(b.1) waste that was characteristic waste but that has been treated so that it is no longer characteristic waste, if the waste may not be disposed of by land disposal under subsection 79 (1),

See:  O. Reg. 461/05, ss. 1 (22), 29 (5).

but does not include waste from the servicing of motor vehicles at a retail motor vehicle service station or service facility that has a written agreement for the collection and management of such waste with a waste management system approved under Part V of the Act for the purposes and does not include waste from,

(c) a nursing home under the Nursing Homes Act,

(d) a home under the Homes for the Aged and Rest Homes Act,

(e) a home for special care under the Homes for Special Care Act,

(f) the professional office of a member of the Royal College of Dental Surgeons of Ontario, or

(g) the professional office of a member of the College of Physicians and Surgeons of Ontario;

“Toxicity Characteristic Leaching Procedure” means the Toxicity Characteristic Leaching Procedure, Method 1311, that appears in United States Environmental Protection Agency Publication SW-846 entitled “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, as amended from time to time, or a test method that the Director has approved in writing as equivalent;

“transfer” means physical transfer of possession;

“transfer station” means a waste disposal site used for the purpose of transferring waste from one vehicle to another for transportation to another waste disposal site;

Note:  On January 1, 2007, subsection (1) is amended by adding the following definition:

“treatment code” means a code listed as a treatment code in Schedule 7;

See:  O. Reg. 461/05, ss. 1 (24), 29 (3).

“vehicle” includes a rail car;

“vehicle sewage holding tank” means a device permanently mounted in or on a vehicle to receive in-vehicle sewage produced in the vehicle;

“waste generation facility” means those facilities, equipment and operations that are involved in the production, collection, handling or storage of waste at a site;

“waste transportation system” means those facilities, equipment and operations that are involved in transporting waste beyond the boundaries of a site or from site to site;

“waste-derived fuel” means waste that,

(a) is hazardous waste, liquid industrial waste, waste described in clause (p), (q), (r), (s), (t) or (u) of the definition of “hazardous waste” or waste described in clause (d) of the definition of “liquid industrial waste”,

(b) contains not more than 5 milligrams per kilogram arsenic, not more than 2 milligrams per kilogram cadmium, not more than 10 milligrams per kilogram chromium, not more than 50 milligrams per kilogram lead, not more than 2 milligrams per kilogram PCBs (as defined in Regulation 362 of the Revised Regulations of Ontario, 1990) and not more than 1,500 milligrams per kilogram total halogens,

(c) has a flash point of at least 38° Celsius as determined by the Tag Closed Cup Tester (ASTM D-56-79), the Setaflash Closed Cup Tester (ASTM D-3243-77 or ASTM D-3278-78), the Pensky-Martens Closed Cup Tester (ASTM D-93-79) or an equivalent test method approved by the Director,

(d) has a quality as fuel not worse than commercially available low grade fuel, and

(e) is located at or destined for a waste-derived fuel site, where it will be wholly utilized as a fuel or fuel supplement in a combustion unit;

“waste-derived fuel site” means a waste disposal site where waste-derived fuel is wholly utilized as a fuel or fuel supplement in a combustion unit used principally for functions other than waste management and the site may include blending or bulking facilities but may not include facilities for treatment or processing of waste-derived fuel generated off the site;

“woodwaste” means waste,

(a) that is wood or a wood product, including tree trunks, tree branches, leaves and brush,

(b) that is not contaminated with chromated copper arsenate, ammoniacal copper arsenate, pentachlorophenol or creosote, and

(c) from which easily removable hardware, fittings and attachments, unless they are predominantly wood or cellulose, have been removed,

but does not include,

(d) an upholstered article, or

(e) an article to which a rigid surface treatment is affixed or adhered, unless the rigid surface treatment is predominantly wood or cellulose;

“woodwaste combustor site” means a waste disposal site where woodwaste is incinerated or wholly utilized as a fuel or fuel supplement in a combustion unit.  R.R.O. 1990, Reg. 347, s. 1; O. Reg. 240/92, s. 1; O. Reg. 501/92, s. 1; O. Reg. 555/92, s. 1; O. Reg. 105/94, s. 1; O. Reg. 190/94, s. 1; O. Reg. 512/95, s. 1; O. Reg. 157/98, s. 1; O. Reg. 460/99, s. 1; O. Reg. 558/00, s. 1 (1-11); O. Reg. 501/01, s. 1; O. Reg. 323/02, s. 1; O. Reg. 461/05, s. 1.

(2) For the purpose of this Regulation, a waste is derived from a hazardous waste if it is produced from the hazardous waste by blending, stabilization, processing, treatment or disposal.  O. Reg. 558/00, s. 1 (12).

Designation and Exemption of Wastes

2. (1) The following are designated as wastes:

1. Dust suppressant.

2. Inert fill.

3. Processed organic waste.

4. Material that consists solely of waste from one or more of the categories set out in Schedule 1, 2 or 3 of Ontario Regulation 101/94 and that either,

i. has been separated from other kinds of waste at the source of the material, or

ii. comes from a waste disposal site.

5. Rock fill or mill tailings from a mine.

6. Waste-derived fuel.

7. Hazardous waste.

8. Hauled liquid industrial waste.

9. Used tires that have not been refurbished for road use.

10. Stationary refrigerant waste.

11. Mobile refrigerant waste.

12. Woodwaste.

13. Municipal waste.

14. Residue from an industrial, manufacturing or commercial process or operation, if the residue leaves the site where the process or operation is carried on.

15. Hauled sewage.  O. Reg. 555/92, s. 2; O. Reg. 105/94, s. 2 (1); O. Reg. 128/98, s. 1; O. Reg. 157/98, s. 2.

(2) The following materials from the time they leave a construction site or a demolition site are designated wastes:

1. Brick.

2. Corrugated cardboard.

3. Concrete.

4. Drywall.

5. Steel.

6. Wood.  O. Reg. 105/94, s. 2 (2).

(3) A designation set out in subsection (2) does not apply to material leaving a construction site or demolition site that is being delivered,

(a) to the vendor of the material for resale as construction material;

(b) to permanent premises of the person undertaking the construction or the person on whose behalf the construction is undertaken, for use as construction material by or for the person; or

(c) to permanent premises of the person undertaking the demolition or the person on whose behalf the demolition is undertaken, for use as construction material by or for the person.  O. Reg. 105/94, s. 2 (2).

3. (1) The following wastes are exempted from Part V of the Act and this Regulation:

1. Agricultural wastes.

2. Condemned animals or parts thereof at a plant licensed under the Meat Inspection Act (Ontario) or an establishment operating under the Meat Inspection Act (Canada).

3. Dead animals to which the Dead Animal Disposal Act applies

4. Revoked:  O. Reg. 157/98, s. 3.

5. Inert fill.

6. Rock fill or mill tailings from a mine.

7. Material set out in subsection (2).  R.R.O. 1990, Reg. 347, s. 3; O. Reg. 105/94, s. 3 (1); O. Reg. 157/98, s. 3.

(2) The material referred to in paragraph 7 of subsection (1) is any of the following:

1. Municipal waste, hazardous waste or liquid industrial waste, other than used or shredded or chipped tires, transferred by a generator for direct transportation to a site,

i. to be wholly used at the site in an ongoing agricultural, commercial, manufacturing or industrial process or operation used principally for functions other than waste management if the process or operation does not involve combustion or land application of the waste,

ii. to be promptly packaged for retail sale to meet a realistic market demand, or

iii. to be offered for retail sale to meet a realistic market demand.

2. Municipal waste, consisting solely of waste from a single category of waste set out in Schedule 1, 2 or 3 of Ontario Regulation 101/94, transferred by a generator and destined for,

i. a waste disposal site that, but for the exemption in section 5 of Ontario Regulation 101/94, would be a municipal waste recycling site to which Part IV of that regulation applies and that is located at a manufacturing establishment that uses all the output, other than residues, of the site, or

ii. a site for use at the site in an ongoing agricultural, commercial, manufacturing or industrial process or operation used principally for functions other than waste management if the process or operation does not involve combustion or land application of the waste.

3. Residue remaining after metal is recovered from wire and cable and transferred by a generator for direct transportation to a site at which it will be processed for recovery of metal and plastic using a process that does not involve combustion of the residue or any part of the residue.

4. Chipped wood, other than chipped painted wood, chipped treated wood or chipped laminated wood, intended for use as ground cover.

5. Waste wood, other than painted wood, treated wood or laminated wood, transferred by a generator and destined for a site at which it is to be chipped for eventual use as ground cover.

6. Pickle liquor transferred by a generator for direct transportation to a site at which it is to be wholly utilized as a treatment chemical in,

i. a sewage works that is subject to the Ontario Water Resources Act,

i.1 a sewage works outside Ontario, if the utilization of pickle liquor for this purpose is acceptable to the environmental regulatory authority in the jurisdiction where the sewage works is located, or

ii. a wastewater treatment facility that discharges into a sanitary sewer.

7. Solid photographic waste that contains silver, including spent chemical recovery cartridges that contain silver, transferred by a generator and destined for a site at which it is to be processed for recovery of silver.  O. Reg. 105/94, s. 3 (2); O. Reg. 128/98, s. 2 (1); O. Reg. 461/05, s. 2.

(3) Despite subsection (1), material referred to in subparagraph i of paragraph 1 of subsection (2) is exempt from Part V of the Act and this Regulation only if the carrier has in his or her possession while transporting the material a document from the owner or operator of the site to which the material is being transported agreeing to accept the material, specifying what use will be made of it and stipulating that the process or operation described in that subparagraph is ongoing at the time the material is being transported.  O. Reg. 105/94, s. 3 (2).

(4) In subsection (2),

“ground cover” means,

(a) mulch,

(b) landscaping material, or

(c) surfacing material for,

(i) trails or walkways for pedestrian use,

(ii) trails or paths for use by livestock or other animals,

(iii) pens or enclosures for livestock or other animals,

(iv) playgrounds,

(v) parking areas, or

(vi) private roads.  O. Reg. 128/98, s. 2 (2).

Classification and Exemption of Waste Disposal Sites

4. Revoked:  O. Reg. 105/94, s. 4.

5. (1) The following waste disposal sites are exempt from Part V of the Act and this Regulation:

1. On-site incinerators at the site of a veterinary hospital.

2. On-site garbage grinders.

3. Derelict motor vehicle sites.

4. Incinerators at the site of a crematorium within the meaning of the Cemeteries Act.  R.R.O. 1990, Reg. 347, s. 5 (1).

(2) Dust suppression sites designated in a certificate of approval or provisional certificate of approval for a dust suppression waste management system and established and operated in accordance therewith are exempt from the requirement to have a waste disposal site certificate of approval or provisional certificate of approval.  R.R.O. 1990, Reg. 347, s. 5 (2).

(3) Revoked:  O. Reg. 555/92, s. 4.

(4) No person shall use waste oil as a dust suppressant.  R.R.O. 1990, Reg. 347, s. 5 (4).

5.1 (1) A waste disposal site that is the subject of an application for a certificate of approval referred to in subsection 30 (1) of the Act is exempt from the requirements of subsection 30 (1) of the Act, but only in relation to the application, and only if the application is not for an approval for,

(a) the deposit of waste at a dump;

(b) the landfilling of waste; or

(c) the incineration of waste.  O. Reg. 457/93, s. 1.

(2) For the purposes of clause (1) (a), the deposit of waste at a dump does not include the handling, storing, transferring, treating or processing of waste at a dump.  O. Reg. 457/93, s. 1.

5.2 (1) In this section,

“service area”, with respect to a landfilling site, means the geographical area from which the site is permitted, under a certificate of approval or a provisional certificate of approval, to receive municipal waste.  O. Reg. 299/94, s. 1.

(2) A municipality that owns or operates a landfilling site is exempt from sections 27, 30 and 32 of the Act with respect to increasing the service area of the site if the additional area from which the site will receive municipal waste is,

(a) within the boundaries of the local municipality in which the site is located or, if the upper tier municipality in which the local municipality is located is exercising the power to provide land filling sites for the local municipality, within the boundaries of that upper tier municipality;

(b) within the boundaries of the municipality that owns or operates the site;

(c) within the boundaries of an area that is not organized as a municipality and that abuts the municipality that owns or operates the site; or

(d) within the boundaries of a separated municipality that abuts the municipality that owns or operates the site.  O. Reg. 299/94, s. 1.

(3) A municipality that owns or operates a landfilling site is exempt from sections 30 and 32 of the Act with respect to an increase in the rate at which municipal waste may be received at the site from areas within its service area.  O. Reg. 299/94, s. 1.

(4) If a municipality owns or operates a landfilling site that has been filled in accordance with an exemption under this section, the municipality is exempt from sections 27, 30 and 32 of the Act with respect to increasing the service area of another landfilling site that it owns and operates if the additional area from which the other site will receive municipal waste is part or all of the area from which the filled site received municipal waste.  O. Reg. 299/94, s. 1; O. Reg. 461/05, s. 3.

(5) A person, other than a municipality, who owns or operates a landfilling site is exempt from sections 27, 30 and 32 of the Act with respect to increasing the service area of the site if,

(a) the additional area from which the site will receive municipal waste is within the boundaries of a municipality from which it already receives municipal waste;

(b) the municipality referred to in clause (a) is a local municipality or an upper tier municipality that is exercising the power to provide landfilling sites for the local municipality; and

(c) the site has a certificate of approval or a provisional certificate of approval, the terms or conditions of which establish a periodic quantity limit for deliveries of waste to the landfilling site.  O. Reg. 299/94, s. 1.

(6) A person, other than a municipality, who owns or operates a landfilling site is exempt from sections 30 and 32 of the Act with respect to increasing the service area of the site if,

(a) the additional area from which the site will receive municipal waste is within the boundaries of a municipality from which it already receives municipal waste;

(b) the municipality referred to in clause (a) is a local municipality or an upper tier municipality that is exercising the power to provide landfilling sites for the local municipality;

(c) the site has a certificate of approval or a provisional certificate of approval;

(d) the Director imposes a term or condition establishing a periodic quantity limit for deliveries of waste to the site; and

(e) the periodic quantity limit is equivalent to an estimate based on existing terms or conditions defining a service area for the site or on historic deliveries to the site.  O. Reg. 299/94, s. 1.

6. (1) For the purposes of subsection (3),

(a) each tire weighing less than twelve kilograms is one tire unit;

(b) each tire weighing twelve kilograms or more is the number of tire units that results from dividing twelve into the number of kilograms that the tire weighs; and

(c) each twelve kilograms of chipped or shredded tires is a tire unit.  R.R.O. 1990, Reg. 347, s. 6 (1).

(2) Steel that has been separated from other components of tires in the process of chipping or shredding tires shall not be counted for the purposes of clause (1) (c).  R.R.O. 1990, Reg. 347, s. 6 (2).

(3) Section 27 of the Act does not apply in respect of a used tire site if,

(a) the total number of tire units at the site is less than 5,000;

(b) the total volume of the piles of tire units at the site is less than 300 cubic metres; and

(c) used, chipped or shredded tires are not incinerated or buried at the site.  O. Reg. 183/92, s. 1; O. Reg. 555/92, s. 5 (1).

(4) Despite subsection (3), the only persons exempted from section 40 of the Act for depositing waste at a used tire site described in subsection (3) are persons belonging to one of the following classes:

1. The owner of the land on which the site is located.

2. A person acting with the written permission of the owner of the land on which the site is located.

3. The operator of a motor vehicle service station acting in the ordinary course of the service station business, in the case of a site that is accessory to the station.

4. A person acting with the permission of the operator of a motor vehicle service station and in the ordinary course of the service station business, in the case of a site that is accessory to the station.  O. Reg. 183/92, s. 1; O. Reg. 555/92, s. 5 (2).

(5) Revoked:  O. Reg. 183/92, s. 1.

Classification and Exemption of Waste Management Systems

7. Section 27 of the Act does not apply to vehicle sewage holding tanks.  O. Reg. 157/98, s. 4.

8. (1) The following waste management systems are exempt from Part V of the Act and this Regulation:

1. Individual collection systems.

2. Marine craft waste disposal systems.  R.R.O. 1990, Reg. 347, s. 8 (1).

(2) Waste generation facilities are exempt from the requirement to have a waste management system certificate of approval in respect of the production, collection, handling and temporary storage of waste.  R.R.O. 1990, Reg. 347, s. 8 (2); O. Reg. 105/94, s. 6.

Note:  On March 31, 2006, subsection (2) is revoked.  See:  O. Reg. 461/05, ss. 4, 29 (2).

(3) Section 27 of the Act does not apply in respect of trucks for hauling used tires.  R.R.O. 1990, Reg. 347, s. 8 (3).

9. The standards, procedures and requirements set out in this Regulation do not apply to the extent that terms and conditions set out in a certificate of approval or a provisional certificate of approval issued under section 39 of the Act impose different standards, procedures or requirements.  R.R.O. 1990, Reg. 347, s. 9.

10. No person shall use, operate or establish a waste management system or waste disposal site or any part of either of them except in accordance with the applicable prescribed standards.  R.R.O. 1990, Reg. 347, s. 10.

Standards for Waste Disposal Sites

11. The following are prescribed as standards for the location, maintenance and operation of a landfilling site:

1. Access roads and on-site roads shall be provided so that vehicles hauling waste to and on the site may travel readily on any day under all normal weather conditions.

2. Access to the site shall be limited to such times as an attendant is on duty and the site shall be restricted to use by persons authorized to deposit waste in the fill area.

3. Drainage passing over or through the site shall not adversely affect adjoining property and natural drainage shall not be obstructed.

4. Drainage that may cause pollution shall not, without adequate treatment, be discharged into watercourses.

5. Waste shall be placed sufficiently above or isolated from the maximum water table at the site in such manner that impairment of groundwater in aquifers is prevented and sufficiently distant from sources of potable water supplies so as to prevent contamination of the water, unless adequate provision is made for the collection and treatment of leachate.

6. Where necessary to isolate a landfilling site and effectively prevent the egress of contaminants, adequate measures to prevent water pollution shall be taken by the construction of berms and dykes of low permeability.

7. Where there is a possibility of water pollution resulting from the operation of a landfilling site, samples shall be taken and tests made by the owner of the site to measure the extent of egress of contaminants and, if necessary, measures shall be taken for the collection and treatment of contaminants and for the prevention of water pollution.

8. The site shall be located a reasonable distance from any cemetery.

9. Adequate and proper equipment shall be provided for the compaction of waste into cells and the covering of the cells with cover material.

10. Where climatic conditions may prevent the use of the site at all times, provisions shall be made for another waste disposal site which can be used during such periods.

11. Where required for accurate determination of input of all wastes by weight, scales shall be provided at the site or shall be readily available for use.

12. All waste disposal operations at the site shall be adequately and continually supervised.

13. Waste shall be deposited in an orderly manner in the fill area, compacted adequately and covered by cover material by a proper landfilling operation.

14. Procedures shall be established for the control of rodents or other animals and insects at the site.

15. Procedures shall be established, signs posted, and safeguards maintained for the prevention of accidents at the site.

16. The waste disposal area shall be enclosed to prevent entry by unauthorized persons and access to the property shall be by roadway closed by a gate capable of being locked.

17. A green belt or neutral zone shall be provided around the site and the site shall be adequately screened from public view.

18. Whenever any part of a fill area has reached its limit of fill, a final cover of cover material shall be placed on the completed fill and such cover shall be inspected at regular intervals over the next ensuing period of two years and where necessary action shall be taken to maintain the integrity and continuity of the cover materials.

19. Scavenging shall not be permitted.  R.R.O. 1990, Reg. 347, s. 11.

12. The following are prescribed as standards for the location, maintenance and operation of an incineration site:

1. The location of the incineration site shall be selected so as to reduce the effects of nuisances such as dust, noise and traffic.

2. Fly-ash that is hazardous waste and that results from the incineration of waste that is neither hazardous waste nor liquid industrial waste shall be kept separate from incinerator ash and disposed of or otherwise dealt with separately from incinerator ash.

3. Fly-ash that is hazardous waste and that results from the incineration of waste that is neither hazardous waste nor liquid industrial waste shall only be disposed of at,

i. the TRICIL Limited landfilling site located on Lot 9, Concession 10, Township of Moore, County of Lambton, or

ii. a landfilling site authorized to accept fly-ash that is hazardous waste and that results from the incineration of waste that is neither hazardous waste nor liquid industrial waste by the terms of,

A. a certificate of approval or provisional certificate of approval issued after the 1st day of January, 1990, or

B. an amendment to a certificate of approval or provisional certificate of approval made after the 1st day of January, 1990.

4. The incinerator shall be located,

i. so that it is accessible for the transportation of wastes thereto without nuisance,

ii. taking into account meteorological considerations to minimize environmental effects, and

iii. so that the services and utilities required for the operation of the incinerator are available, including facilities for the disposal of residue and of quenching and scrubbing water.

5. The design and capacity of the incinerator shall be in accordance with accepted engineering practices and of a type and size adequate to efficiently process the quantities of waste that may be expected, so that a minimum volume of residue is obtained, the putrescible materials remaining as residue are reduced to a minimum and a minimum of air pollution results.

6. The following equipment shall be provided as necessary for particular applications:

i. Scales for the accurate determination of the input of all wastes by weight.

ii. A storage pit or other storage facilities.

iii. A crane or other means of removing waste from the pit or other storage facilities.

iv. Means of controlling dusts and odours.

v. Such instruments as may be necessary for the efficient operation of an incinerator.

7. The incineration site shall include an unloading area properly enclosed and of sufficient size for the intended operation.

8. Access roads shall be provided for vehicles hauling waste to the incineration site.

9. On-site fire protection shall be provided and, where possible, arrangements shall be made with a fire department or municipality for adequate fire fighting services in case of an emergency.

10. Scavenging shall not be permitted.  R.R.O. 1990, Reg. 347, s. 12.

12.1 Revoked:  O. Reg. 512/95, s. 2.

13. The following are prescribed as standards for the location, maintenance and operation of a dump:

1. The fill area shall not be subject to flooding and shall be so located that no direct drainage leads to a watercourse.

2. The site shall be at least one-quarter of a mile from the nearest dwelling.

3. The site shall be at least two hundred yards from the nearest public road.

4. The site shall be at least 100 feet from any watercourse, lake or pond.

5. The site shall not be on land covered by water.

6. Signs shall be posted stating requirements for the operation of the dump, including measures for the control of vermin and insect infestation.

7. The site shall be so located and operated as to reduce to a minimum the hazards resulting from fire.

8. The operator of a dump shall apply such cover material at such intervals as is necessary to prevent harm or material discomfort to any person.

9. Scavenging shall not be permitted.  R.R.O. 1990, Reg. 347, s. 13.

14. (1) Subject to subsection (2), no dump shall be established or operated in a city, borough, town, separated town, township, village or police village in any county, regional municipality or the County of Haliburton.  R.R.O. 1990, Reg. 347, s. 14 (1).

(2) A dump may be established in the following parts of Ontario:

1. The townships of Albemarle, Eastnor, Lindsay and St. Edmunds, in the County of Bruce.

2. The townships of Barrie, Bedford, Clarendon and Miller, Howe Island, Kennebec, Olden and Palmerston and North and South Canonto, in the County of Frontenac.

3. The townships of Bangor, Wicklow and McClure, Carlow, Dungannon, Elzevir and Grimsthorpe, Herschel, Limerick, Madoc, Marmora and Lake, Mayo, Monteagle, Tudor and Cashel, and Wollaston, in the County of Hastings.

4. The townships of Dalhousie and North Sherbrooke, Darling, Lavant, North Burgess, and South Sherbrooke, in the County of Lanark.

5. The townships of Asphodel, Belmont and Methuen, Chandos, Ennismore, Galway and Cavendish, and Harvey, in the County of Peterborough.

6. The townships of Bagot and Blithfield, Brougham, Brudenell and Lyndoch, Griffith and Matawatchan, Head, Clara, and Maria, North Algona, Radcliffe, Raglan, Sebastopol, and South Algona, in the County of Renfrew.

7. The townships of Carden, Dalton, and Laxton, Digby and Longford, in the County of Victoria.

8. The Improvement District of Bicroft, the townships of Anson, Hindon and Minden, Cardiff, Dysart, Bruton, Clyde, Dudley, Eyre, Guilford, Harburn, Harcourt and Havelock, Glamorgan, Lutterworth, Monmouth, Sherborne, McClintock and Livingstone, and Snowdon and Stanhope, in the County of Haliburton.  R.R.O. 1990, Reg. 347, s. 14 (2).

(3) No dump shall be established or operated in the following parts of the territorial districts of Ontario:

1. The City of Sault Ste. Marie, the towns of Blind River, Bruce Mines, Thessalon and Elliot Lake, and the villages of Hilton Beach and Iron Bridge, in the Territorial District of Algoma.

2. The City of Timmins, the towns of Cochrane, Hearst, Iroquois Falls, Kapuskasing and Smooth Rock Falls, and the townships of Glackmeyer, Tisdale and Whitney, in the Territorial District of Cochrane.

3. The towns of Dryden, Keewatin, Kenora, and Sioux Lookout, and the townships of Jaffray and Melick, in the Territorial District of Kenora.

4. The towns of Gore Bay and Little Current, in the Territorial District of Manitoulin.

5. That part of The District Municipality of Muskoka that, on the 31st day of December, 1970, was the towns of Bala, Bracebridge, Gravenhurst and Huntsville, and the villages of Port Carling, Port Sydney and Windermere.

6. The City of North Bay, the towns of Cache Bay, Mattawa and Sturgeon Falls, and the townships of Bonfield, East Ferris, Field and Springer, in the Territorial District of Nipissing.

7. The towns of Kearney, Parry Sound, Powassan and Trout Creek, the villages of Burk’s Falls, Magnetawan, Rosseau, South River and Sundridge, and the townships of Foley, McDougall, North Himsworth, and South Himsworth, in the Territorial District of Parry Sound.

8. The towns of Fort Frances and Rainy River, and the Township of Atikokan, in the Territorial District of Rainy River.

9. That part of The Regional Municipality of Sudbury and the Territorial District of Sudbury that, on the 31st day of December, 1972, was the City of Sudbury, the towns of Capreol, Coniston, Copper Cliff, Espanola, Levack, Lively, Massey and Webbwood, and the townships of Balfour, Falconbridge, and Neelon and Garson, in the Territorial District of Sudbury.

10. The City of Thunder Bay, the Town of Geraldton and the townships of Beardmore, Manitowadge, Neebing, Nipigon, Oliver, Paipoonge, Schreiber, Shuniah, and Terrace Bay, and the improvement districts of Nakina and Red Rock, in the Territorial District of Thunder Bay.

11. The towns of Charlton, Cobalt, Englehart, Haileybury, Kirkland Lake, Latchford, and New Liskeard, the Village of Thornloe, and the townships of Armstrong, Bucke, Larder Lake and McGarry, in the Territorial District of Timiskaming.  R.R.O. 1990, Reg. 347, s. 14 (3).

Note:  On March 31, 2006, the Regulation is amended by adding the following section:

14.0.1 If hazardous waste is being handled, stored, treated or disposed of at a waste disposal site or transferred to a waste disposal site, no person shall cause or permit the hazardous waste to be mixed, blended, bulked or in any other way intermingled with any other waste or material, unless the mixing, blending, bulking or other intermingling is in accordance with a certificate of approval or provisional certificate of approval issued under Part V of the Act for the waste disposal site.  O. Reg. 461/05, s. 5.

See:  O. Reg. 461/05, ss. 5, 29 (2).

14.1 The following are prescribed as standards for the location, maintenance and operation of waste disposal sites for hauled sewage:

1. A person shall not apply hauled sewage in any manner that permits it to enter a watercourse or drainage ditch.

2. A person shall not apply hauled sewage in any manner that results in runoff leaving the site.

3. If the operator of a proposed site is not the owner of the land on which the site is to be located, the operator must, before applying for a certificate of approval for the site, obtain written authorization from the owner for the proposed use of the site.  O. Reg. 157/98, s. 5.

14.2 (1) Subject to subsection (3), no person shall cause or permit waste from a portable toilet to be applied to land or otherwise deposited at a site except,

(a) at a waste disposal site that has been issued a certificate of approval or provisional certificate of approval permitting the temporary storage of hauled sewage and from which the hauled sewage is not subsequently removed and disposed of except in accordance with this section;

(b) at a waste disposal site that has been issued a certificate of approval or provisional certificate of approval permitting the disposal of hauled sewage for drying and requiring the dried residue to be periodically removed and disposed of at a waste disposal site approved to accept the dried residue;

(c) at a landfilling site that has been issued a certificate of approval or provisional certificate of approval for the final disposal of hauled sewage;

(d) at a sewage works that has been approved under section 53 of the Ontario Water Resources Act to receive sanitary sewage or hauled sewage; or

(e) at a site that has been issued a certificate of approval or provisional certificate of approval permitting the processing of waste and that processes waste in a manner that ensures that the waste meets all of the following requirements after it has been processed:

(i) the concentration of Escherichia coli (E. coli) in the waste is not more than 2x106 colony forming units per gram of total solids (dry weight),

(ii) the concentration in the waste of each metal listed in the Table to this section is not more than the maximum concentration set out for that metal in the Table,

(iii) the pH value of the waste is not less than 6.0,

(iv) the waste has been passed through a screen and contains no more than 0.5 per cent dry weight of plastic objects and no more than 2 per cent dry weight of other non-biodegradable objects, including, but not limited to, glass and metal objects.  O. Reg. 326/03, s. 1.

(2) Subsection (1) applies despite anything contained in a certificate of approval or a provisional certificate of approval that was issued before this section comes into force.  O. Reg. 326/03, s. 1.

(3) No person shall cause or permit waste from a portable toilet to be disposed of at an organic soil conditioning site unless,

(a) the organic soil conditioning site has been issued a certificate of approval or provisional certificate of approval permitting the spreading or application of treated waste from a portable toilet;

(b) the waste has been treated so that the concentration of Escherichia coli (E. coli) is not more than 2x106 colony forming units per gram of total solids (dry weight);

(c) the concentration in the waste of each metal listed in the Table to this section is not more than the maximum concentration set out for that metal in the Table;

(d) the pH value of the treated waste is not less than 6.0; and

(e) the waste has been passed through a screen and contains no more than 0.5 per cent dry weight of plastic objects and no more than 2 per cent dry weight of other non-biodegradable objects, including, but not limited to, glass and metal objects.  O. Reg. 326/03, s. 1.

TABLE

 

Item

Metal

Maximum Permissible Concentration (In mg/kg Of Solids, Dry Weight)

1.

Arsenic

170

2.

Cadmium

34

3.

Cobalt

340

4.

Chromium-

2,800

5.

Copper

1,700

6.

Mercury

11

7.

Molybdenum

94

8.

Nickel

420

9.

Lead

1,100

10.

Selenium

34

11.

Zinc

4,200

O. Reg. 326/03, s. 1.

15. The following are prescribed as standards for the location, maintenance and operation of an organic soil conditioning site:

1. The site shall be so located that it is an adequate distance from any watercourse, as determined by the land slope, to prevent direct surface drainage to the watercourse.

2. The site shall be at least 300 feet from the nearest individual dwelling.

3. The site shall be at least 1,500 feet from any area of residential development.

4. The site shall be so located that the maximum level of the ground water table at the site is at a sufficient distance below the surface to prevent the impairment of ground water in aquifers as determined by the permeability of the soil.

5. The site shall be at least 300 feet from any water wells.

6. No processed organic waste shall be applied to the site during any period in which conditions are such that surface runoff is likely to occur taking into account land slope, soil permeability and the climatic conditions of the area.

7. The site shall be established only on land that is, or is intended to be, used for pasture, fallow or the growing of forage crops,

i. during the current growing season, or

ii. where application of the processed organic waste is made sometime after the current growing season, to the end of the subsequent growing season.

8. Berms and dykes of low permeability shall be constructed on the site where necessary to isolate the site and effectively prevent the egress of contaminants.  R.R.O. 1990, Reg. 347, s. 15.

Standards for Waste Management Systems

16. (1) The following are prescribed as standards for the operation of a waste management system:

1. All waste collection vehicles and waste carriers shall be so constructed as to enable waste to be transferred safely and without nuisance from storage containers to the vehicle.

2. Bodies of waste collection vehicles and waste carriers shall be so constructed as to withstand abrasion and corrosion from the waste.

3. Bodies of waste collection vehicles and waste carriers shall be leakproof and covered where necessary to prevent the emission of offensive odours, the falling or blowing of waste material from the vehicles or the release of dust or other air-borne materials that may cause air pollution.

4. Valves that are part of a waste transportation vehicle used for transporting liquid industrial waste or hazardous waste shall have a locking mechanism and shall be locked when the vehicle contains the waste and the driver of the vehicle is not in attendance.

5. Whenever liquid industrial waste or hazardous waste is being transferred to or from a waste transportation vehicle, the driver of the vehicle must be present unless the generator or receiver is present.

Note:  On March 31, 2006, subsection (1) is amended by adding the following paragraph:

5.1 If hazardous waste is being transferred to or from a waste transportation vehicle or is being transported in a waste transportation vehicle, no person shall cause or permit the hazardous waste to be mixed, blended, bulked or in any other way intermingled with any other waste or material, unless,

i. the mixing, blending, bulking or other intermingling is in accordance with a certificate of approval or provisional certificate of approval issued under Part V of the Act for the receiving facility named in the manifest that is related to the waste transportation vehicle’s load, and the carrier has, accompanying the load, a document from the owner or operator of the receiving facility agreeing to accept the mixed, blended, bulked or otherwise intermingled waste, or

ii. the mixing, blending, bulking or other intermingling is done in accordance with a certificate of approval or provisional certificate of approval issued under Part V of the Act for a waste transportation system that the waste transportation vehicle is part of.

See:  O. Reg. 461/05, ss. 6, 29 (2).

6. A waste transportation vehicle used for transporting liquid industrial waste or hazardous waste shall be clearly marked with the name and number appearing on the certificate of approval or provisional certificate of approval that authorizes the transportation.

7. Where a waste transportation vehicle is used for transporting liquid industrial waste or hazardous waste, a copy of the certificate of approval or provisional certificate of approval that authorizes that transportation shall be kept in the vehicle.

8. A waste transportation vehicle used for transporting liquid industrial waste or hazardous waste shall be constructed, maintained, operated and marked or placarded in accordance with the applicable requirements of the Transportation of Dangerous Goods Act (Canada).

9. The driver of a waste transportation vehicle used for the transportation of liquid industrial waste or hazardous waste shall be trained in,

i. the operation of the vehicle and waste management equipment,

ii. relevant waste management legislation, regulations and guidelines,

iii. major environmental concerns pertaining to the waste to be handled,

iv. occupational health and safety concerns pertaining to the waste to be handled, and

v. emergency management procedures for the wastes to be handled.

10. A waste transportation vehicle used for transporting municipal waste shall be clearly marked with the name and number appearing on the certificate of approval or provisional certificate of approval that authorizes the transportation.

11. Where a waste transportation vehicle is used for transporting municipal waste, a copy of the certificate of approval or provisional certificate of approval that authorizes that transportation shall be kept in the vehicle.

12. If the waste management system is used for hauled sewage, the operator of the system shall ensure that every tank used for the transportation of hauled sewage has inscribed in plain view the words “Sewage Waste” in letters that are at least 15 centimetres in height, unless the tank bears a company designation in letters of at least that height that clearly indicates the nature of the contents.

13. If the waste management system is used for hauled sewage, the operator of the system shall ensure that any part of the system that comes into contact with hauled sewage is not used for the collection, handling, treatment, transportation, storage or processing of any material other than hauled sewage or a material approved in writing by the Director.

14. A person shall not discharge or permit the discharge of hauled sewage from a tank that is part of a waste management system to the ground except in accordance with terms and conditions contained in a certificate of approval, provisional certificate of approval or order.  R.R.O. 1990, Reg. 347, s. 16; O. Reg. 105/94, s. 7 (1); O. Reg. 157/98, s. 6 (1).

(2) Paragraphs 10 and 11 of subsection (1) do not apply,

(a) if the vehicle is owned and operated by or operated exclusively for a municipality or the Crown; or

(b) if the vehicle is operating as part of a waste management system that is exempt from the requirement of having a certificate of approval or provisional certificate of approval.  O. Reg. 105/94, s. 7 (2).

(3) Paragraph 13 of subsection (1) does not apply if,

(a) the part of the waste management system that came into contact with hauled sewage is not used for the collection, handling, treatment, transportation, storage or processing of hazardous waste, hauled liquid industrial waste or liquids for human or animal consumption;

(b) the part of the system that came into contact with hauled sewage is used for the collection, handling, treatment, transportation, storage or processing of other liquid material and the owner or operator of the system obtains every approval required for that purpose; and

(c) the part of the system that came into contact with hauled sewage is cleaned, to the satisfaction of any person to whom the other liquid material will be transferred, before that part of the system is used for the collection, handling, treatment, transportation, storage or processing of the other liquid material.  O. Reg. 157/98, s. 6 (2).

(4) If, pursuant to subsection (3), a part of a waste management system that came into contact with hauled sewage is used for the collection, handling, treatment, transportation, storage or processing of other liquid material, a person shall not use that part of the system again for hauled sewage unless it, and any other part of the system that was contaminated during the collection, handling, treatment, transportation, storage or processing of the other liquid material, has been cleaned to the satisfaction of the Director.  O. Reg. 157/98, s. 6 (2).

(5) The operator of a waste management system for hauled sewage shall,

(a) keep daily records of the premises from which hauled sewage is collected and the amounts of sewage collected from those premises;

(b) keep daily records of the disposal site or disposal sites at which hauled sewage is discharged or disposed of and the amounts of hauled sewage discharged or disposed of at those sites; and

(c) keep the daily records required by clauses (a) and (b) available for review by the Director, as the Director may require, for a period of at least two years after the calendar year to which the records relate.  O. Reg. 157/98, s. 6 (2).

16.1 The following are prescribed as standards for the operation and maintenance of vehicle sewage holding tanks:

1. A person shall not discharge or permit the discharge of effluent from a vehicle sewage holding tank to the surface of the ground or into ground water, surface water, a piped water supply, a well water supply, a watercourse or a drainage ditch.

2. A person shall not discharge or permit the discharge of effluent from a vehicle sewage holding tank except from a place on or part of the tank, or from a piping system connected to the tank, that is designed to discharge effluent.

3. The owner and the operator of a vehicle sewage holding tank shall ensure that insects and animals are prevented from gaining access to sewage in the tank.

4. The owner and the operator of a vehicle sewage holding tank shall ensure that the tank does not discharge micro organisms of intestinal origin into the natural environment in a manner that may be hazardous to human health.

5. The owner and the operator of a vehicle sewage holding tank shall ensure that no gas is discharged into a building or structure from the tank or a piping system connected to the tank except in a manner for which the tank or piping system was designed.

6. The owner and the operator of a vehicle sewage holding tank shall ensure that the tank does not receive any waste other than in-vehicle sewage produced in the vehicle.

7. The owner and the operator of a vehicle sewage holding tank shall ensure that the tank and any piping system connected to the tank are maintained in good operating condition.  O. Reg. 157/98, s. 7.

Management of Asbestos Waste

17. No person shall manage asbestos waste except in accordance with the following:

1. No person shall cause or permit asbestos waste to leave the location at which it is generated except for the purpose of transporting it, in accordance with paragraph 2, to a waste disposal site, the operator of which has agreed to accept it and has been advised as to its anticipated time of arrival.

2. Asbestos waste transported to a waste disposal site shall,

i. be in a rigid, impermeable, sealed container of sufficient strength to accommodate the weight and nature of the waste, or

ii. where the asbestos waste is being transported in bulk, be transported by means of a waste management system operating under a certificate of approval or provisional certificate of approval that specifically authorizes the transportation of asbestos waste in bulk.

3. Where a container referred to in subparagraph i of paragraph 2 is a cardboard box, the waste must be sealed in a six-mil polyethylene bag placed within the box.

4. Every container referred to in subparagraph i of paragraph 2 must be free from punctures, tears or leaks.

5. The external surfaces of every container referred to in subparagraph i of paragraph 2 and of every vehicle or vessel used for the transport of asbestos waste must be free from asbestos waste.

6. Both sides of every vehicle used for the transportation of asbestos waste and every container referred to in subparagraph i of paragraph 2 must display thereon in large, easily legible letters that contrast in colour with the background the word “CAUTION” in letters not less than ten centimetres in height and the words:

CONTAINS ASBESTOS FIBRES

Avoid Creating Dust and Spillage

Asbestos May be Harmful To Your Health

Wear Approved Protective Equipment.

7. Asbestos waste being transported from the location at which it is generated,

i. shall be transported,

A. by a driver trained in the management of asbestos waste,

B. as directly as may be practicable, to the waste disposal site at which disposal of the asbestos waste is intended to take place,

ii. shall not be transferred to a transfer station or other waste disposal site where disposal of the asbestos waste will not take place, but it may be transported to a waste disposal site operating under a certificate of approval or provisional certificate of approval that specifically authorizes acceptance and processing of asbestos waste,

iii. shall not be transported with any other cargo in the same vehicle,

iv. shall not be transported in a compaction type waste haulage vehicle,

v. where it is being transported in cardboard boxes, shall be in an enclosed vehicle,

vi. shall be properly secured and covered with a suitable tarpaulin or net if it is transported in a vehicle that is not enclosed, and

vii. shall be transported only in vehicles equipped with emergency spill cleanup equipment including a shovel, a broom, wetting agent, protective clothing, a supply of six-mil polyethylene bags, bag closures and personal respiratory equipment.

8. During the transportation or unloading thereof, any asbestos waste that is loose or in a container that is punctured, broken or leaking shall be packaged, immediately on discovery, in a six-mil polyethylene bag.

9. Where containers of asbestos waste are being unloaded, the unloading shall be carried out so that no loose asbestos or punctured, broken or leaking containers of asbestos waste are landfilled.

10. Asbestos waste may be deposited only at locations in a landfilling site that have been adapted for the purpose of receiving asbestos waste or are otherwise suitable for that purpose.

11. Asbestos waste may be deposited at a landfilling site only while the depositing is being supervised by the operator of the site or a person designated by the operator for the purpose and the person supervising is not also operating machinery or the truck involved.

12. Where asbestos waste is deposited, as set out in paragraph 10, at least 125 centimetres of garbage or cover material must be placed forthwith over the deposited asbestos waste in such a manner that direct contact with compaction equipment or other equipment operating on the site is avoided.

13. Every person handling asbestos waste or containers of asbestos waste, supervising the unloading of asbestos waste in bulk or cleaning asbestos waste residues from containers, vehicles or equipment shall wear protective clothing and personal respiratory equipment while so doing.

14. Protective clothing that has been or is suspected of having been in contact with asbestos waste shall be changed at the site of the exposure and either properly disposed of as asbestos waste or washed at the end of the working day.

15. Disposable protective clothing shall not be reused.

16. Every person directly or indirectly involved in the transportation, handling or management of asbestos waste shall take all precautions necessary to prevent asbestos waste from becoming airborne.  R.R.O. 1990, Reg. 347, s. 17.

Note:  On March 31, 2006, the Regulation is amended by adding the following sections:

Waste Generation Facilities

17.1 (1) Sections 27, 40 and 41 of the Act do not apply to a waste generation facility in respect of the activities set out in subsection (2), to the extent that those activities relate to,

(a) waste that was produced at the waste generation facility, other than PCB waste; or

(b) waste that came legally to the waste generation facility but was not produced at the facility, other than PCB waste, soil or a soil mixture.  O. Reg. 461/05, s. 7.

(2) The following activities are the activities referred to in subsection (1):

1. The production, collection, handling or temporary storage of municipal waste.

2. The production, collection, handling or temporary storage of subject waste.

3. The processing of waste, if the processing does not involve,

i. the combustion or land application of municipal waste, hazardous waste or liquid industrial waste,

ii. the mixing, blending, bulking or other intermingling of waste or other material with characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed, or

iii. the processing of soil.

4. The processing of municipal waste at an on-site incinerator that, pursuant to subsection 28 (1) of this Regulation, is exempt from the operation of section 27 of the Act.

5. The processing of characteristic waste or listed waste, if the processing involves the mixing, blending, bulking or other intermingling of waste or other material with the characteristic waste or listed waste, and,

i. the processing will, by itself or in conjunction with other processing, permit the land disposal of the characteristic waste or listed waste under section 75, 76, 77, 78 or 79, or

ii. the mixed, blended, bulked or otherwise intermingled waste is to be transported to a receiving facility, the mixing, blending, bulking or other intermingling is in accordance with a certificate of approval or provisional certificate of approval issued under Part V of the Act for the receiving facility, and the operator of the waste generation facility has, at the waste generation facility, a document from the owner or operator of the receiving facility agreeing to accept the mixed, blended, bulked or otherwise intermingled waste.

6. The processing of waste so that it becomes exempt from Part V of the Act and this Regulation under paragraph 7 of subsection 3 (1).

7. The introduction of waste into, and the processing of waste in preparation for the introduction of the waste into,

i. a sewage works that is subject to the Ontario Water Resources Act or that was established before August 3, 1957, or

ii. a sewage system regulated under Part 8 of Ontario Regulation 403/97 (Building Code) made under the Building Code Act, 1992.

8. The packaging or offering of waste for retail sale to meet a realistic market demand, and the processing of waste, if the processing is for the purpose of packaging or offering the waste for retail sale to meet a realistic demand.

9. The transfer to a waste transportation vehicle of,

i. municipal waste, or

ii. subject waste, other than characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed.

10. The transfer to a waste transportation vehicle of characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed, if the transfer does not involve the mixing, blending, bulking or other intermingling of the characteristic waste or listed waste with any other waste or material.

11. The transfer to a waste transportation vehicle of characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed, if the transfer involves the mixing, blending, bulking or other intermingling of the characteristic waste or listed waste with any other waste or material and,

i. the mixing, blending, bulking or other intermingling is in accordance with a certificate of approval or provisional certificate of approval issued under Part V of the Act for the receiving facility named in the manifest that is related to the waste transportation vehicle’s load, and the carrier has, accompanying the load, a document from the owner or operator of the receiving facility agreeing to accept the mixed, blended, bulked or otherwise intermingled waste, or

ii. the mixing, blending, bulking or other intermingling is done in accordance with a certificate of approval or provisional certificate of approval issued under Part V of the Act for a waste transportation system that the waste transportation vehicle is part of.  O. Reg. 461/05, s. 7.

(3) Subsection (1) does not apply to a waste generation facility if waste management is the principal function of the waste generation facility.  O. Reg. 461/05, s. 7.

17.2 If a waste generation facility to which subsection 17.1 (1) applies stores subject waste, the operator and the owner of the facility shall ensure that it is operated in accordance with the following rules:

1. Subject waste must be stored, handled and maintained so as to prevent,

i. leaks or spills of the waste, or

ii. damage to or deterioration of the container in which the waste is stored.

2. Subject waste must not be stored for a period exceeding 24 months unless an application for a certificate of approval respecting the storage of subject waste by the waste generation facility has been made and not yet determined.

3. The first time that subject waste is stored at the waste generation facility for more than 90 days, a notice must be given to the Regional Director, within five business days after the 90th day of storage, that,

i. describes, as accurately as possible, the nature, amount and location of subject waste stored, or expected to be stored in the future, at the waste generation facility for more than 90 days, and

ii. indicates how frequently subject waste is expected to be stored in the future at the waste generation facility for more than 90 days.

4. If notice is given under paragraph 3, written notice must be given to the Regional Director of,

i. any change in the information referred to in paragraph 3, within five business days after the change, or

ii. the closure of the waste generation facility, within five business days after the closure.

5. If subject waste is stored at the waste generation facility for more than 90 days, a record must be made of the following information within five business days after the 90th day of storage:

i. The name and waste number of the waste.

ii. The quantity of the waste.

iii. The manner in which the waste is stored.

iv. The reasons for storing the waste.

v. The anticipated time and manner of disposal of the waste.

6. A record made under paragraph 5 must be updated as often as necessary to ensure that it contains information that is current to within five business days.

7. A record made or updated under paragraph 5 or 6 must be retained at the location where subject waste is stored.

8. A record made or updated under paragraph 5 or 6 must be retained until the date that the subject waste is no longer stored, and for at least two years after that date.  O. Reg. 461/05, s. 7.

See:  O. Reg. 461/05, ss. 7, 29 (2).

Generator Registration

18. (1) Every generator who operates a waste generation facility that is involved in the production, collection, handling or storage of subject waste shall,

(a) before transferring any subject waste from that waste generation facility, submit an initial Generator Registration Report to the Director in respect of the facility; and

(b) on or before February 15 in each year, submit an annual Generator Registration Report to the Director in respect of each waste generation facility operated by the generator.  O. Reg. 501/01, s. 2 (1).

Note:  On January 1, 2007, section 18 is amended by adding the following subsection:

(1.1) Subsection (1) applies to waste produced, collected, handled or stored at the waste generation facility that is subject waste and that is characteristic waste or listed waste, even if the waste ceases to be hazardous waste while it is at the facility.  O. Reg. 461/05, s. 8 (1).

See:  O. Reg. 461/05, ss. 8 (1), 29 (3).

(2) Every report referred to in subsection (1) or (6) shall be in the form or format provided or approved by the Ministry, shall comply with the Manual and shall contain such data, analysis and information as will enable the Director to satisfy himself or herself as to the quality and nature of the waste.  O. Reg. 501/01, s. 2 (1).

Note:  On January 1, 2007, subsection (2) is revoked and the following substituted:

(2) Every report referred to in subsection (1) or (6) shall be in the form or format provided or approved by the Ministry, shall comply with the Manual and shall contain the data, analysis and other information necessary to enable the Director to satisfy himself or herself of the following:

1. The quality, quantity and nature of the waste.

2. The required treatment for the waste and the planned treatment for the waste.

3. The intended manner and location of the disposal of the waste or, if the waste is not to be disposed, the use to which the waste will be put.

4. Compliance with all applicable legal requirements.  O. Reg. 461/05, s. 8 (2).

See:  O. Reg. 461/05, ss. 8 (2), 29 (3).

(3) Upon receipt of an initial or annual Generator Registration Report and the required fee, the Director shall post on the Ministry website a generator registration document for the waste generation facility that is the subject of the Generator Registration Report setting out the date of the posting, the name of the generator, a generator registration number and the applicable waste numbers accepted by the Director.  O. Reg. 501/01, s. 2 (1).

(4) A generator registration document posted under subsection (3) is valid until the earlier of the posting of a revised or subsequent generator registration document in respect of the same waste generation facility and February 15 of the year after the year in which the document was posted.  O. Reg. 501/01, s. 2 (1).

(5) A generator registration document issued to a generator before January 1, 2002 remains valid until the earlier of the posting of a generator registration document under subsection (3) and February 15, 2002.  O. Reg. 501/01, s. 2 (1).

Note:  On January 1, 2007, subsection (5) is revoked.  See:  O. Reg. 461/05, ss. 8 (3), 29 (3).

(6) Where there is a change from the information submitted in an initial Generator Registration Report or in the most recent annual Generator Registration Report or any previous supplementary Generator Registration Reports in respect of the generator’s name, address or telephone number, the name of the contact for the generator, the name of the responsible official for the generator or the addition of subject wastes or where there is a significant change from such previously submitted information in respect of the description or physical or chemical characteristics of the subject wastes, the generator who submitted the applicable report shall send a supplementary Generator Registration Report to the Director within 15 days after the change.  O. Reg. 501/01, s. 2 (1).

Note:  On January 1, 2007, subsection (6) is revoked and the following substituted:

(6) If there is any change from the information submitted in an initial Generator Registration Report, the most recent annual Generator Registration Report or any previous supplementary Generator Registration Reports, the generator shall submit a supplementary Generator Registration Report to the Director within 15 days after the change.  O. Reg. 461/05, s. 8 (4).

(6.1) A generator who submits an initial, annual or supplementary Generator Registration Report to the Director shall make a record of all data, analysis and other information used in the preparation of the report and shall keep the record at the waste generation facility for at least three years.  O. Reg. 461/05, s. 8 (4).

See:  O. Reg. 461/05, ss. 8 (4), 29 (3).

(7) Upon receipt of a supplementary Generator Registration Report that relates to a valid generator registration document, the Director shall post on the Ministry website a revised generator registration document.  O. Reg. 501/01, s. 2 (1).

(7.1) No generator shall transfer a particular subject waste from a waste generation facility to a waste transportation system unless a valid generator registration document for that waste generation facility with a waste number for that particular subject waste is posted on the Ministry website.  O. Reg. 501/01, s. 2 (1).

(7.2) In all transfers of subject waste under this Regulation, every generator shall use the generator registration number issued in respect of the waste generation facility from which the subject waste is being transferred and the applicable waste numbers set out in the Manual.  O. Reg. 501/01, s. 2 (1).

(8) Every generator shall keep a record of the subject waste disposed of at the waste generation facility including the name, waste number, quantity and disposition of the waste.  R.R.O. 1990, Reg. 347, s. 18 (8).

(9) A record referred to in subsection (8) may be disposed of after two years.  R.R.O. 1990, Reg. 347, s. 18 (9).

(10) When any subject waste is retained at a waste generation facility for a period longer than three months, the generator, unless there is a waste disposal site certificate of approval or provisional certificate of approval in respect of the facility, shall submit a report to the Regional Director of the Ministry within five business days after the three month period which report shall comply with the Manual and shall include the name and waste number of the waste, the quantity involved, the manner in which it is stored, the reasons for the retention and the anticipated time and manner of disposal of the waste.  R.R.O. 1990, Reg. 347, s. 18 (10); O. Reg. 460/99, s. 2 (3).

Note:  On January 1, 2007, subsection (10) is revoked.  See:  O. Reg. 461/05, ss. 8 (5), 29 (3).

(11) Every generator who transfers subject waste to a waste transportation system shall orally report to the Director any transferred subject waste that the generator is not able, within four weeks, to confirm was delivered to the intended receiving facility or to another receiving facility approved to accept the waste.  R.R.O. 1990, Reg. 347, s. 18 (11).

(12) In unusual circumstances, such as a spill, a process aberration or upset, or the circumstances described in subsection 22 (2), where a generator discovers that a generator registration number or a waste number is needed to comply with this Regulation in the disposal of subject waste, the Regional Director of the Ministry or an alternate named by him or her may assign a generator registration number or accept a waste number identified by the generator.  R.R.O. 1990, Reg. 347, s. 18 (12).

(13) Where a generator registration number is assigned under subsection (12), subsection (7.1) does not apply and subsections (1) and (2) shall be complied with within ninety days.  O. Reg. 501/01, s. 2 (2).

(14) Where a waste number is accepted under subsection (12), subsection (7.1) does not apply.  O. Reg. 501/01, s. 2 (2).

(14.1) Subsection (11) does not apply if an electronic manifest is used.  O. Reg. 501/01, s. 2 (2).

(15) For purposes of this section,

“liquid waste” means waste that has a slump of more than 150 millimetres using the Test Method for the Determination of Liquid Waste (slump test) set out in Schedule 5.  O. Reg. 558/00, s. 2.

Note:  On January 1, 2007, the definition of “liquid waste” is amended by striking out “set out in Schedule 5” at the end and substituting “set out in Schedule 9”.  See:  O. Reg. 461/05, ss. 8 (6), 29 (3).

Manifests — Generator Requirements

19. (1) No generator shall permit subject waste to pass from the generator’s control or to leave the waste generation facility except,

(a) by transfer of the subject waste to a waste transportation system operating under a certificate of approval or provisional certificate of approval and where the generator has completed a manifest in respect of the waste in accordance with the Manual and this Regulation; or

(b) by direct discharge to a sewage works subject to the Ontario Water Resources Act or established before August 3, 1957 or into a sewage system regulated under Part 8 of the Building Code made under the Building Code Act, 1992.  R.R.O. 1990, Reg. 347, s. 19 (1); O. Reg. 460/99, s. 3; O. Reg. 501/01, s. 3.

(2) No generator shall transfer subject waste to a waste transportation system unless the subject waste is so packaged or marked that it meets the transport requirements of the Transportation of Dangerous Goods Act (Canada).  R.R.O. 1990, Reg. 347, s. 19 (2).

Manifests — Carrier Requirements

20. (1) Every carrier shall report to the Director the number of every intact manifest supplied to the carrier that is lost, spoiled or used other than in accordance with this Regulation.  R.R.O. 1990, Reg. 347, s. 20.

(2) Every carrier shall return to the Director every intact manifest or partial manifest supplied to the carrier that is not used for the purposes of this Regulation because it has been spoiled or completed erroneously or for any other reason, within three days after the carrier has decided not to use the manifest.  O. Reg. 501/01, s. 4.

20.1 (1) No carrier shall have possession of subject waste in Ontario unless the waste was accepted from a generator and waste generation facility for which a valid generator registration document for that waste generation facility with a waste number for that particular subject waste is posted on the Ministry website.  O. Reg. 501/01, s. 5.

(2) Subsection (1) does not apply in respect of subject waste,

(a) accepted from a generator to whom section 18 does not apply; or

(b) accepted from outside Ontario for the purpose of being transported for transfer to a receiving facility outside Ontario.  O. Reg. 501/01, s. 5.

21. (1) No carrier shall have possession of subject waste unless the carrier has, accompanying the waste, a manifest in respect of the waste, completed by the generator in accordance with the Manual and this Regulation, except during a transfer while the manifest is being completed by a generator or receiver.  R.R.O. 1990, Reg. 347, s. 21 (1); O. Reg. 460/99, s. 4.

(2) For purposes of subsection (1), a manifest is not completed by a generator in accordance with this Regulation if it contains an obvious error.  R.R.O. 1990, Reg. 347, s. 21 (2).

(3) A printed copy of an electronic manifest with sections A and B completed shall be sufficient for the purposes of subsection (1).  O. Reg. 501/01, s. 6.

22. (1) No carrier shall permit subject waste to pass from the carrier’s control except in accordance with this Regulation.  R.R.O. 1990, Reg. 347, s. 22 (1).

(2) A carrier, with the specific approval of a Regional Director of the Ministry or an alternate named by him or her, may transfer subject waste in Ontario to another vehicle in the same waste transportation system or to a waste transportation system operating under a certificate of approval or provisional certificate of approval or to a receiving facility to alleviate a dangerous situation.  R.R.O. 1990, Reg. 347, s. 22 (2).

(3) Where a truckload or less of subject waste has been transferred by a generator to a waste transportation system, the carrier shall promptly transport the waste to the receiving facility named in the manifest related to that load unless the carrier is permitted to do otherwise by subsection (2) or section 27.  R.R.O. 1990, Reg. 347, s. 22 (3).

Manifests — Transport within Ontario

23. (1) This section applies where a generator transfers subject waste in Ontario to a waste transportation system for transport to a receiving facility in Ontario and, for the purpose of this section, “generator” includes a carrier to whom subsection 22 (2) applies.  R.R.O. 1990, Reg. 347, s. 23 (1).

(2) Where subject waste is transferred to a waste transportation system by a generator and a paper manifest is used,

(a) for each truckload or part thereof transferred, the carrier shall complete section B (Carrier) of an intact manifest and give the manifest, at the time of the transfer, to the generator; and

(b) for each truckload or part thereof transferred, the generator shall obtain from the carrier the intact manifest, with section B completed, and shall,

(i) at the time of the transfer, complete section A (Generator) in accordance with the Manual,

(ii) remove Copy 1 (White) and return it to the Director within three working days after the transfer,

(iii) remove Copy 2 (Green) and retain it for a period of two years, and

(iv) return the remaining four copies of the manifest to the carrier at the time of the transfer.  O. Reg. 558/00, s. 3; O. Reg. 501/01, s. 7 (1).

(2.1) Where subject waste is transferred to a waste transportation system by a generator and an electronic manifest is used, for each truckload or part thereof transferred, at the time of the transfer,

(a) the generator shall give the carrier electronic access to the manifest;

(b) the carrier shall electronically complete section B (Carrier) of the manifest; and

(c) the generator shall,

(i) electronically complete section A (Generator) of the manifest in accordance with the Manual,

(ii) give the receiver electronic access to the manifest,

(iii) electronically submit the manifest, with sections A and B completed, to the Director, and

(iv) if requested by the carrier, print a paper copy of the manifest, as submitted under subclause (iii), and give it to the carrier.  O. Reg. 501/01, s. 7 (2).

(3) A carrier may transfer subject waste,

(a) with the specific approval of a Regional Director of the Ministry or an alternate named by him or her, to another vehicle of the same waste transportation system, to a waste transportation system operating under a certificate of approval or provisional certificate of approval or to a specified receiving facility as mentioned in clause (b), (c) or (d) to alleviate a dangerous situation;

(b) to a waste disposal site operating under a certificate of approval or provisional certificate of approval authorizing acceptance of the waste;

(c) with the consent of the owner of the sewage works, to a sewage works for which an approval under the Ontario Water Resources Act has been issued and that is not in contravention of the approval; or

(d) to a waste-derived fuel site having a combustion unit operating under a certificate of approval issued under section 9 of the Act authorizing acceptance and combustion of the waste.  R.R.O. 1990, Reg. 347, s. 23 (3).

(4) Every carrier transferring waste under subsection (3) shall, at the time of the transfer, give the receiver the remaining four parts of the paper manifest, or the number of the electronic manifest, completed for that load of waste.  O. Reg. 501/01, s. 7 (3).

(5) Where a transfer of subject waste takes place under subsection (3) and a paper manifest is used, the receiver shall obtain from the carrier the remaining four parts of the manifest completed for that load and shall,

(a) at the time of the transfer, complete section C (Receiver) of the remaining four parts of the manifest;

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the transfer;

(c) remove Copy 4 (Pink) of the manifest and return it to the carrier at the time of the transfer;

(d) retain Copy 5 (Blue) of the manifest for two years; and

(e) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the transfer.  R.R.O. 1990, Reg. 347, s. 23 (5); O. Reg. 501/01, s. 7 (4).

(5.1) Where a transfer of subject waste takes place under subsection (3) and an electronic manifest is used, the receiver shall obtain from the carrier the number of the manifest completed for that load, shall electronically access the manifest and shall, at the time of the transfer,

(a) electronically complete section C (Receiver) of the manifest; and

(b) electronically submit the manifest, with sections A, B and C completed, to the Director.  O. Reg. 501/01, s. 7 (5).

(6) Every carrier transferring waste under subsection (3) shall, prior to leaving the site of the transfer, obtain from the receiver of the waste Copy 4 (Pink) of the manifest referred to under clause (5) (c) and shall retain it for a period of two years.  R.R.O. 1990, Reg. 347, s. 23 (6).

(7) Where a paper manifest is used, every carrier who is the operator of a waste transportation system for which a certificate of approval or provisional certificate of approval as a dust suppression waste management system is issued may deposit for the purpose of dust suppression, in accordance with the approval, dust suppressant at a dust suppression site designated in the approval and, where that is done, shall,

(a) at the time of completion of the deposit, complete section C (Receiver) of the remaining four parts of the applicable manifest received under subclause (2) (b) (iv);

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the deposit;

(c) retain Copy 4 (Pink) of the manifest for two years; and

(d) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the deposit.  R.R.O. 1990, Reg. 347, s. 23 (7); O. Reg. 501/01, s. 7 (6).

(8) Where an electronic manifest is used, every carrier described in subsection (7) may deposit for the purpose of dust suppression, in accordance with the approval described in subsection (7), dust suppressant at a dust suppression site designated in the approval and, where that is done, shall, as quickly as is reasonably possible following completion of the deposit,

(a) electronically access the manifest completed for that load;

(b) electronically complete section C (Receiver) of the manifest; and

(c) electronically submit the manifest, with sections A, B and C completed, to the Director.  O. Reg. 501/01, s. 7 (7).

Manifests — Transport out of Ontario

24. (1) This section applies where a generator transfers subject waste in Ontario to a waste transportation system for transport to a receiving facility outside Ontario.  R.R.O. 1990, Reg. 347, s. 24 (1).

(2) Where subject waste is transferred for transport to a receiving facility in a Canadian jurisdiction, a manifest issued under the Transportation of Dangerous Goods Act (Canada) or an equivalent manifest issued by a Canadian jurisdiction may be used for purposes of compliance with this Regulation.  R.R.O. 1990, Reg. 347, s. 24 (2).

(3) Where subject waste is transferred for transport to a receiving facility in a Canadian jurisdiction and the laws of that jurisdiction require submission to authorities in that jurisdiction of the equivalent of Copy 1 or 3 of a manifest, submission to the Director of a photocopy of the copy submitted or of a copy retained may be substituted for the requirement to submit Copy 1 or 3 of a manifest.  R.R.O. 1990, Reg. 347, s. 24 (3).

(4) Where subject waste is transferred to a waste transportation system by a generator and a paper manifest is used,

(a) for each truckload or portion thereof transferred, the carrier shall complete section B (Carrier) of an intact manifest and give the manifest, at the time of the transfer, to the generator; and

(b) for each truckload or portion thereof transferred, the generator shall obtain from the carrier the intact manifest, with section B completed, and shall,

(i) at the time of the transfer, complete section A (Generator) in accordance with the Manual,

(ii) remove Copy 1 (White) and return it to the Director within three working days after the transfer,

(iii) remove Copy 2 (Green) and retain it for two years, and

(iv) return the remaining four copies of the manifest to the carrier at the time of the transfer.  R.R.O. 1990, Reg. 347, s. 24 (4); O. Reg. 460/99, s. 6; O. Reg. 501/01, s. 8 (1).

(4.1) Where subject waste is transferred to a waste transportation system by a generator and an electronic manifest is used, for each truckload or part thereof transferred, at the time of the transfer,

(a) the generator shall give the carrier electronic access to the manifest;

(b) the carrier shall electronically complete section B (Carrier) of the manifest; and

(c) the generator shall,

(i) electronically complete section A (Generator) of the manifest in accordance with the Manual,

(ii) give the receiver electronic access to the manifest,

(iii) electronically submit the manifest, with sections A and B completed, to the Director, and

(iv) if requested by the carrier, print a paper copy of the electronic manifest, as submitted under subclause (iii), and give it to the carrier.  O. Reg. 501/01, s. 8 (2).

(5) No carrier shall transport subject waste out of Ontario destined for a receiving facility outside Ontario unless the carrier has reason to believe the intended receiver is willing to complete section C (Receiver) of the applicable manifest completed for that load of waste and, in the case of an electronic manifest, electronically submit the completed manifest to the Director.  R.R.O. 1990, Reg. 347, s. 24 (5); O. Reg. 501/01, s. 8 (3).

(6) Where a paper manifest is used, every carrier transferring subject waste to a receiving facility outside Ontario shall, at the time of the transfer, give the receiver the remaining four parts of the manifest for completion of section C (Receiver).  O. Reg. 501/01, s. 8 (4).

(7) Where a paper manifest is used, every carrier who transfers waste under subsection (6) shall,

(a) return Copy 3 (Yellow) of the manifest to the Director within three working days after the transfer;

(b) retain Copy 4 (Pink) of the manifest for two years; and

(c) remove Copy 6 (Brown) of the manifest and return it to the generator indicated on the manifest within three working days after the transfer.  R.R.O. 1990, Reg. 347, s. 24 (7); O. Reg. 501/01, s. 8 (5).

(8) Every manifest referred to in subsection (7) shall have section C (Receiver) completed by the receiver.  R.R.O. 1990, Reg. 347, s. 24 (8).

(9) Where an electronic manifest is used, every carrier who transfers subject waste under subsection (6) shall, at the time of the transfer, give the receiver the number of the electronic manifest completed for that load of waste and request that the receiver electronically access the manifest and, at the time of the transfer,

(a) electronically complete section C (Receiver) of the manifest; and

(b) electronically submit the manifest, with sections A, B and C completed, to the Director.  O. Reg. 501/01, s. 8 (6).

(10) Every carrier shall notify the Director forthwith of the number of the electronic manifest, the name of the receiver, if it is not the same as that set out in section A of the manifest, and the date of the transfer to the receiver, where the carrier is aware that the receiver has not complied with a request made under subsection (9).  O. Reg. 501/01, s. 8 (6).

Manifests — Transport into Ontario

25. (1) This section applies where subject waste is transferred outside Ontario to a waste transportation system for transport to a receiving facility in Ontario.  R.R.O. 1990, Reg. 347, s. 25 (1).

(2) Where subject waste is transferred in Canada for transport to a receiving facility in Ontario, a manifest under the Transportation of Dangerous Goods Act (Canada) or any equivalent manifest issued by a Canadian jurisdiction may be used for purposes of compliance with this Regulation.  R.R.O. 1990, Reg. 347, s. 25 (2).

(3) Where a paper manifest is used, no carrier shall bring subject waste into Ontario for purposes of transport to a receiving facility in Ontario unless,

(a) Revoked:  O. Reg. 501/01, s. 9 (2).

(b) for each truckload or portion thereof to be transferred, the carrier completed section B (Carrier) of an intact manifest and gave it, at the time of the transfer, to the generator for completion of section A (Generator) and return to the carrier; and

(c) the applicable manifest with section B (Carrier) completed by the carrier and section A (Generator) completed by the generator accompanies the waste.  R.R.O. 1990, Reg. 347, s. 25 (3); O. Reg. 501/01, s. 9 (1, 2).

(3.1) Where an electronic manifest is used, no carrier shall bring subject waste into Ontario for purposes of transport to a receiving facility in Ontario unless, for each truckload or portion thereof to be transferred, at the time of the transfer from the generator,

(a) the carrier electronically completed section B (Carrier) of the manifest; and

(b) the generator electronically completed section A (Generator) of the manifest and electronically submitted the manifest, with sections A and B completed, to the Director.  O. Reg. 501/01, s. 9 (3).

(4) Where a paper manifest is used, every carrier who brings subject waste into Ontario for transfer to a receiving facility in Ontario shall forward to the Director, within three working days after the out of province transfer, Copy 1 (White) of the manifest showing the generator registration number and the applicable waste number.  O. Reg. 501/01, s. 9 (4).

(5) A carrier may transfer subject waste,

(a) to a waste disposal site operating under a certificate of approval or provisional certificate of approval authorizing acceptance of the waste;

(b) with the consent of the owner of the sewage works, to a sewage works for which an approval under the Ontario Water Resources Act has been issued, and that is not in contravention of the approval; or

(c) to a waste-derived fuel site having a combustion unit operating under a certificate of approval issued under section 9 of the Act authorizing acceptance and combustion of the waste.  R.R.O. 1990, Reg. 347, s. 25 (5).

(6) Every carrier transferring waste under subsection (5) shall, at the time of the transfer, give the receiver the remaining four parts of the paper manifest completed in respect of the waste or number of the electronic manifest completed in respect of the waste, as the case may be.  O. Reg. 501/01, s. 9 (5).

(7) Where a transfer of subject waste takes place under subsection (5) and a paper manifest is used, the receiver shall obtain from the carrier the remaining four parts of the manifest completed in respect of that load of waste and shall,

(a) at the time of the transfer, complete section C (Receiver) of the remaining four parts of the manifest;

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the transfer;

(c) remove Copy 4 (Pink) of the manifest and return it to the carrier at the time of the transfer;

(d) retain Copy 5 (Blue) of the manifest for two years; and

(e) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the transfer.  R.R.O. 1990, Reg. 347, s. 25 (7); O. Reg. 501/01, s. 9 (6).

(7.1) Where a transfer of subject waste takes place under subsection (5) and an electronic manifest is used, the receiver shall obtain from the carrier the number of the manifest completed for that load, shall electronically access the manifest and shall, at the time of the transfer,

(a) electronically complete section C (Receiver) of the manifest; and

(b) electronically submit the manifest, with sections A, B and C completed, to the Director.  O. Reg. 501/01, s. 9 (7).

(8) Where a paper manifest is used, every carrier who has transferred waste under subsection (5) shall, prior to leaving the site of the transfer, obtain from the receiver Copy 4 (Pink) of the manifest and shall retain it for two years.  O. Reg. 501/01, s. 9 (8).

(9) Where a paper manifest is used, every carrier who is the operator of a waste transportation system for which a certificate of approval or provisional certificate of approval as a dust suppression waste management system is issued may deposit for the purpose of dust suppression, in accordance with the approval, dust suppressant at a dust suppression site designated in the approval and, where that is done, shall,

(a) at the time of completion of the deposit, complete section C (Receiver) of the remaining four parts of the manifest accompanying the waste;

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the deposit;

(c) retain Copy 4 (Pink) of the manifest for two years; and

(d) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the deposit.  R.R.O. 1990, Reg. 347, s. 25 (9); O. Reg. 501/01, s. 9 (9).

(10) Where an electronic manifest is used, every carrier described in subsection (9) may deposit for the purpose of dust suppression, in accordance with the approval described in subsection (9), dust suppressant at a dust suppression site designated in the approval and, where that is done, shall, as quickly as is reasonably possible following completion of the deposit,

(a) electronically access the manifest completed for that load;

(b) electronically complete section C (Receiver) of the manifest; and

(c) electronically submit the manifest, with sections A, B and C completed, to the Director.  O. Reg. 501/01, s. 9 (10).

Manifests — Transport through Ontario

26. (1) No carrier shall transport through Ontario subject waste from outside Ontario for transfer to a receiving facility outside Ontario unless the generator has with the waste, for each truckload or portion thereof, a manifest, or a paper copy of an electronic manifest, completed in accordance with the requirements of the jurisdiction issuing the manifest.  O. Reg. 501/01, s. 10.

(2) Where this section applies, a manifest issued under the Transportation of Dangerous Goods Act (Canada) or an equivalent manifest issued by a Canadian jurisdiction or a Uniform Hazardous Waste Manifest as prescribed by the United States Environmental Protection Agency may be used for purposes of compliance with this Regulation.  R.R.O. 1990, Reg. 347, s. 26 (2).

Refusals

27. (1) A receiver who refuses to accept a transfer of subject waste shall prepare a refusal report in a form or format provided or approved by the Ministry and return it to the Director within three working days after the refusal.  O. Reg. 501/01, s. 11 (1).

(2) Where a carrier intends to transfer subject waste to a receiving facility and the waste is refused by the intended receiver, the carrier, before attempting to make a different transfer, shall consult and obtain the instructions of the generator, unless written instructions have been provided by the generator in advance and may transfer the waste to a receiving facility indicated in the instructions.  R.R.O. 1990, Reg. 347, s. 27 (2).

(3) If waste is refused by the intended receiver at the receiving facility and if the carrier cannot conveniently make a different transfer in accordance with this Regulation, the carrier may transfer the unadulterated waste to the waste generation facility set out in section A (Generator) of the applicable manifest and the carrier shall, at the time of the transfer, give the generator four parts of the paper manifest or the number of the electronic manifest, as the case may be, that was completed in respect of the waste.  O. Reg. 501/01, s. 11 (2).

(4) Every generator shall accept a transfer of unadulterated subject waste in the circumstances described in subsection (3).  R.R.O. 1990, Reg. 347, s. 27 (4).

(5) Where a transfer of subject waste occurs under subsection (3) and a paper manifest is used, the generator shall obtain from the carrier the remaining four parts of the applicable manifest completed by the generator in accordance with this Regulation and shall,

(a) at the time of the transfer, complete section C (Receiver) of the remaining four parts of the manifest;

(b) return Copy 3 (Yellow) to the Director within three working days after the transfer;

(c) return Copy 4 (Pink) to the carrier at the time of the transfer; and

(d) retain Copy 6 (Brown) for two years.  R.R.O. 1990, Reg. 347, s. 27 (5); O. Reg. 501/01, s. 11 (3).

(5.1) Where a transfer of subject waste occurs under subsection (3) and an electronic manifest is used, the generator shall obtain from the carrier the number of the electronic manifest completed for that load, shall electronically access the manifest and shall, at the time of the transfer,

(a) electronically complete section C (Receiver) of the manifest; and

(b) electronically submit the manifest, with sections A, B and C completed, to the Director.  O. Reg. 501/01, s. 11 (4).

(6) Where a paper manifest is used, every carrier who has transferred waste under subsection (3) shall, prior to leaving the site of the transfer, obtain from the receiver Copy 4 (Pink) of the manifest and shall retain it for two years.  O. Reg. 501/01, s. 11 (5).

(7) A waste generation facility is exempt from the requirement of a waste disposal site certificate of approval under section 27 of the Act in respect of an acceptance of waste under this section.  R.R.O. 1990, Reg. 347, s. 27 (7).

On-Site Incinerators

28. (1) On-site incinerators are exempt from the operation of section 27 of the Act on condition that no hazardous waste or liquid industrial waste is incinerated therein.  R.R.O. 1990, Reg. 347, s. 28 (1).

(2) On-site incinerators are exempt from the requirement of being the subject-matter of a hearing under subsection 30 (1) of the Act.  R.R.O. 1990, Reg. 347, s. 28 (2).

(3) This section does not apply to woodwaste combustor sites or waste-derived fuel sites.  O. Reg. 555/92, s. 7.

Woodwaste Combustor Sites

28.1 (1) A woodwaste combustor site for residential heating is exempt from section 27 of the Act if not more than fifty cubic metres of woodwaste is stored at the woodwaste combustor site at any time.  O. Reg. 555/92, s. 8.

(2) A woodwaste combustor site is exempt from section 27 of the Act if,

(a) not more than 500 cubic metres of woodwaste is stored at the woodwaste combustor site at any time;

(b) not more than 100 tonnes of woodwaste is combusted at the woodwaste combustor site on any day; and

(c) none of the woodwaste stored at the woodwaste combustor site is stored there for more than six months.  O. Reg. 555/92, s. 8.

(3) A woodwaste combustor site is exempt from section 27 of the Act in respect of its use and operation if,

(a) the woodwaste combustor site was first put into operation before the 26th day of September, 1992; and

(b) immediately before the 26th day of September, 1992, no certificate of approval or provisional certificate of approval under Part V of the Environmental Protection Act was required for the use or operation of the woodwaste combustor site.  O. Reg. 555/92, s. 8.

(4) A woodwaste combustor site that is exempt under subsection (3) ceases to be exempt if the use or operation of the woodwaste combustor site changes substantially.  O. Reg. 555/92, s. 8.

(5) A woodwaste combustor site that is exempt under subsection (3) ceases to be exempt at the end of the twelve-month period immediately following the 26th day of September, 1992, if the woodwaste combustor site is in operation on fewer than thirty days during that twelve-month period.  O. Reg. 555/92, s. 8.

28.2 (1) A woodwaste combustor site is exempt from the requirement of being the subject-matter of a hearing under subsection 30 (1) of the Act if not more than 100 tonnes of woodwaste is combusted at the woodwaste combustor site on any day.  O. Reg. 555/92, s. 8.

(2) A woodwaste combustor site is exempt from the requirement of being the subject-matter of a hearing under subsection 30 (1) of the Act if the heat from the combustion is recovered and utilized.  O. Reg. 191/98, s. 1.

Waste-Derived Fuel Sites

28.3 (1) A waste-derived fuel site is exempt from section 27 of the Act if,

(a) the only waste-derived fuel utilized at the waste-derived fuel site is waste-derived fuel that is generated at the waste-derived fuel site and has never left the site; and

(b) not more than ten tonnes of waste-derived fuel is utilized at the waste-derived fuel site on any day.  O. Reg. 555/92, s. 8.

(2) A waste-derived fuel site is exempt from section 27 of the Act in respect of its use and operation if,

(a) the waste-derived fuel site was first put into operation before the 26th day of September, 1992; and

(b) immediately before the 26th day of September, 1992, no certificate of approval or provisional certificate of approval under Part V of the Environmental Protection Act was required for the use or operation of the waste-derived fuel site.  O. Reg. 555/92, s. 8.

(3) A waste-derived fuel site that is exempt under subsection (2) ceases to be exempt if the use or operation of the waste-derived fuel site changes substantially.  O. Reg. 555/92, s. 8.

(4) A waste-derived fuel site that is exempt under subsection (2) ceases to be exempt at the end of the twelve-month period immediately following the 26th day of September, 1992, if the waste-derived fuel site is in operation on fewer than thirty days during that twelve-month period.  O. Reg. 555/92, s. 8.

28.4 A waste-derived fuel site is exempt from the requirement of being the subject-matter of a hearing under subsection 30 (1) of the Act if not more than ten tonnes of waste-derived fuel is utilized at the site on any day.  O. Reg. 555/92, s. 8.

28.5 (1) At a waste-derived fuel site, no person shall mix waste that is not waste-derived fuel with any other waste or material, if the material resulting from the mixing is waste-derived fuel.  O. Reg. 555/92, s. 8.

(2) Subsection (1) does not apply to prohibit the mixing of two or more wastes that are generated at the waste-derived fuel site and have never left the site.  O. Reg. 555/92, s. 8.

Existing Hospital Incinerators

29. (1) Revoked:  R.R.O. 1990, Reg. 347, s. 29 (3); See O. Reg. 323/02, s. 2.

(2) Revoked: R.R.O. 1990, Reg. 347, s. 29 (3); See O. Reg. 323/02, s. 2.

(3) Spent:  O. Reg. 323/02, s. 2.

(4) All existing hospital incinerators that operated under the authority of subsection (1) or (2) and all hospital incinerators operating under a certificate of approval issued before December 6, 2002 must cease operations on or before December 6, 2003.  O. Reg. 323/02, s. 2.

(5) All certificates of approval for hospital incinerators issued before this subsection came into force are revoked on December 6, 2003.  O. Reg. 323/02, s. 2.

Stationary Refrigerant Waste

30. (1) A stationary refrigerant waste collector that collects stationary refrigerant waste shall,

(a) recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers; or

(b) transport it to,

(i) a wholesale dealer in refrigerants,

(ii) a stationary refrigerant waste recycler, or

(iii) a stationary refrigerant waste disposal site with a certificate of approval or provisional certificate of approval to handle stationary refrigerant waste.  R.R.O. 1990, Reg. 347, s. 30 (1); O. Reg. 190/94, s. 2 (1).

(2) A wholesale dealer in refrigerants that receives stationary refrigerant waste shall transport it to,

(a) a stationary refrigerant waste recycler; or

(b) a stationary refrigerant waste disposal site with a certificate of approval or provisional certificate of approval to handle stationary refrigerant waste.  R.R.O. 1990, Reg. 347, s. 30 (2).

(3) A stationary refrigerant waste recycler that receives stationary refrigerant waste shall recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers.  R.R.O. 1990, Reg. 347, s. 30 (3); O. Reg. 190/94, s. 2 (2).

31. (1) A stationary refrigerant waste collector shall keep a written record each time that stationary refrigerant waste is,

(a) removed and collected, at the stationary refrigerant waste collector’s ordinary place of business, from equipment in which refrigerant is used;

(b) received at the stationary refrigerant waste collector’s ordinary place of business, after being removed and collected at another location from equipment in which refrigerant is used; or

(c) transported from or recycled at the stationary refrigerant waste collector’s ordinary place of business.  R.R.O. 1990, Reg. 347, s. 31 (1).

(2) A wholesale dealer in refrigerants shall keep a written record each time that it receives or transports stationary refrigerant waste.  R.R.O. 1990, Reg. 347, s. 31 (2).

(3) A stationary refrigerant waste recycler shall keep a written record each time that it receives or recycles stationary refrigerant waste.  R.R.O. 1990, Reg. 347, s. 31 (3).

(4) A record made under this section shall show,

(a) the date the stationary refrigerant waste was collected, received, transported or recycled;

(b) the source of the stationary refrigerant waste;

(c) the quantity collected, received, transported or recycled;

(d) the type of stationary refrigerant waste; and

(e) what was done with the stationary refrigerant waste.  R.R.O. 1990, Reg. 347, s. 31 (4).

(5) A record made under this section may be disposed of after two years.  R.R.O. 1990, Reg. 347, s. 31 (5).

(6) Revoked:  O. Reg. 190/94, s. 3.

32. (1) A stationary refrigerant waste disposal site that is the ordinary place of business of a stationary refrigerant waste collector or that is operated by a wholesale dealer in refrigerants is exempt from section 27 of the Act if,

(a) access to stationary refrigerant waste is controlled by gates, fencing, attendants or other security measures;

(b) containers in which stationary refrigerant waste is stored are clearly marked as to contents;

(c) stationary refrigerant waste is stored in a location and manner that prevents damage or deterioration;

(d) stored stationary refrigerant waste is readily accessible for inspection by a provincial officer;

(e) there is available, at or near the site, firefighting equipment and spill clean-up and containment equipment appropriate to the quantities and types of stationary refrigerant waste on or likely to be on the site; and

(f) written notice is given to the Director within ninety days after the establishment of the site, specifying the location of the site and the quantities and types of stationary refrigerant waste on or likely to be on the site.  R.R.O. 1990, Reg. 347, s. 32 (1).

(2) A stationary refrigerant waste disposal site is exempt from section 27 of the Act if,

(a) stationary refrigerant waste is removed and collected on the site from equipment in which refrigerant is used; and

(b) the site is not the ordinary place of business of the stationary refrigerant waste collector.  R.R.O. 1990, Reg. 347, s. 32 (2).

33. A stationary refrigerant waste management system is exempt from section 27 of the Act if all stationary refrigerant waste disposal sites used in the system are,

(a) exempt from section 27 of the Act; or

(b) established and operated in accordance with a certificate of approval or provisional certificate of approval under Part V of the Act.  R.R.O. 1990, Reg. 347, s. 33.

34. Section 18 does not apply in respect of subject waste that is stationary refrigerant waste unless,

(a) a stationary refrigerant waste collector transports stationary refrigerant waste directly from the waste generation facility to,

(i) a stationary refrigerant waste recycler, or

(ii) a stationary refrigerant waste disposal site with a certificate of approval or provisional certificate of approval to handle stationary refrigerant waste; or

(b) the waste generation facility is operated by a wholesale dealer in refrigerants.  R.R.O. 1990, Reg. 347, s. 34.

35. Section 19 and sections 21 to 27 do not apply in respect of subject waste that is stationary refrigerant waste being managed in accordance with section 30.  O. Reg. 461/05, s. 9.

Mobile Refrigerant Waste

36. (1) On and after the 1st day of July, 1991, no person shall discharge or permit the discharge of mobile refrigerant waste into the natural environment.  R.R.O. 1990, Reg. 347, s. 36 (1).

(2) On and after the 1st day of July, 1991, a person who removes mobile refrigerant waste from equipment in which refrigerant is used shall collect the mobile refrigerant waste.  R.R.O. 1990, Reg. 347, s. 36 (2).

37. (1) A mobile refrigerant waste collector that collects mobile refrigerant waste shall,

(a) recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers; or

(b) transport it to,

(i) a mobile refrigerant waste recycler, or

(ii) a mobile refrigerant waste disposal site with a certificate of approval or provisional certificate of approval to handle mobile refrigerant waste.  R.R.O. 1990, Reg. 347, s. 37 (1); O. Reg. 190/94, s. 4 (1).

(2) A mobile refrigerant waste recycler that receives mobile refrigerant waste shall recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers.  R.R.O. 1990, Reg. 347, s. 37 (2); O. Reg. 190/94, s. 4 (2).

38. (1) A mobile refrigerant waste collector shall keep a written record each time that mobile refrigerant waste is,

(a) removed and collected, at the mobile refrigerant waste collector’s ordinary place of business, from equipment in which refrigerant is used;

(b) received at the mobile refrigerant waste collector’s ordinary place of business, after being removed and collected at another location from equipment in which refrigerant is used; or

(c) transported from or recycled at the mobile refrigerant waste collector’s ordinary place of business.  R.R.O. 1990, Reg. 347, s. 38 (1).

(2) A mobile refrigerant waste recycler shall keep a written record each time that it receives or recycles mobile refrigerant waste.  R.R.O. 1990, Reg. 347, s. 38 (2).

(3) A record made under this section shall show,

(a) the date the mobile refrigerant waste was collected, transported, received or recycled;

(b) the source of the mobile refrigerant waste;

(c) the quantity collected, transported, received or recycled;

(d) the type of mobile refrigerant waste; and

(e) what was done with the mobile refrigerant waste.  R.R.O. 1990, Reg. 347, s. 38 (3).

(4) A record made under this section may be disposed of after two years.  R.R.O. 1990, Reg. 347, s. 38 (4).

(5) Revoked:  O. Reg. 190/94, s. 5.

39. (1) A mobile refrigerant waste disposal site that is the ordinary place of business of a mobile refrigerant waste collector is exempt from section 27 of the Act if equipment is kept at the site for collecting mobile refrigerant waste removed from equipment in which refrigerant is used.  R.R.O. 1990, Reg. 347, s. 39 (1).

(2) A mobile refrigerant waste disposal site is exempt from section 27 of the Act if,

(a) mobile refrigerant waste is removed and collected on the site from equipment in which refrigerant is used; and

(b) the site is not the ordinary place of business of the mobile refrigerant waste collector.  R.R.O. 1990, Reg. 347, s. 39 (2).

40. A mobile refrigerant waste management system is exempt from section 27 of the Act if all mobile refrigerant waste disposal sites used in the system are,

(a) exempt from section 27 of the Act; or

(b) established and operated in accordance with a certificate of approval or provisional certificate of approval under Part V of the Act.  R.R.O. 1990, Reg. 347, s. 40.

41. Section 18 does not apply in respect of subject waste that is mobile refrigerant waste.  R.R.O. 1990, Reg. 347, s. 41.

42. Section 19 and sections 21 to 27 do not apply in respect of subject waste that is mobile refrigerant waste being managed in accordance with section 37.  O. Reg. 461/05, s. 10.

Selected Waste Depots

42.1-42.17 Revoked:  O. Reg. 298/94, s. 1.

43. In sections 44 to 59,

“lubricant” means crankcase oil, gear oil, transmission fluid and hydraulic fluid;

“selected waste depot” means a depot where selected waste is accepted, handled and stored.  O. Reg. 298/94, s. 1.

44. (1) For the purposes of this section and sections 45 to 59, the products listed in Column A are selected products and the wastes listed in Column B are selected wastes:

 

Column A

Column B

1.

anti-freeze

1.

waste anti-freeze

2.

lubricant

2.

waste lubricant

3.

oil filters

3.

waste oil filters

O. Reg. 298/94, s. 1.

(2) For the purposes of sections 45 to 59, the types of selected product are those listed in Column A of subsection (1) and the types of selected waste are those listed in Column B of subsection (1).  O. Reg. 298/94, s. 1.

45. (1) Sections 47 to 59 apply in relation to selected waste depots that have the following characteristics:

1. The depot is at a location at which a business sells goods or services motor vehicles as one of its primary functions.

2. The depot is managed by a person who owns or has the charge, management or control of the business.

3. The depot is set up to accept, handle and store only selected waste of a type that results from a type of selected product regularly sold at the business.  O. Reg. 298/94, s. 1.

(2) For the purposes of sections 47 to 59, a business and a depot are associated if they have the relationship to each other set out in paragraphs 1, 2 and 3 of subsection (1).  O. Reg. 298/94, s. 1.

46. (1) Sections 27, 40 and 41 of the Act do not apply in relation to a selected waste depot that has the characteristics set out in subsection 45 (1).  O. Reg. 298/94, s. 1.

(2) Sections 18, 19 and 21 to 27 of this Regulation do not apply to require reports or manifests in respect of selected waste stored at or removed from a selected waste depot that has the characteristics set out in subsection 45 (1).  O. Reg. 298/94, s. 1.

(3) Sections 27 and 41 of the Act and section 16 of this Regulation do not apply to the transportation of selected waste by the generator of the waste to a selected waste depot that has the characteristics set out in subsection 45 (1), unless the generator of the waste is required to submit a report under section 18 of this Regulation in respect of the waste.  O. Reg. 298/94, s. 1.

47. (1) Each operator and owner of a selected waste depot shall ensure that no selected waste is accepted at the depot until 15 days after written notice of intent to operate the depot is given to the Chief Fire Official appointed under subsection 1.1.8 of Ontario Regulation 388/97 (Fire Code) made under the Fire Protection and Prevention Act, 1997 and to the Regional Director responsible for the region in which the depot is located.  O. Reg. 298/94, s. 1; O. Reg. 461/05, s. 11.

(2) The notice of intent to operate a selected waste depot shall include the following information:

1. The address of the depot and the location of the depot at the address.

2. The name under which the business associated with the depot carries on business.

3. The types of selected waste to be accepted at the depot.

4. The size, type and number of storage containers to be used at the depot.  O. Reg. 298/94, s. 1.

(3) Each operator and owner of a selected waste depot shall notify the Chief Fire Official and the Regional Director responsible for the region in which the depot is located of any change in respect of the information submitted under this section, no later than 15 days before the change occurs.  O. Reg. 298/94, s. 1.

48. Each operator and owner of a selected waste depot shall ensure, by means of gates, fencing, locks, guards or otherwise, that only people authorized by an operator or owner have access to selected waste at the depot.  O. Reg. 298/94, s. 1.

49. Each operator and owner of a selected waste depot shall ensure that notice of the days and hours during which selected waste will be accepted at the depot is clearly posted at the depot and shall ensure that selected waste is accepted at the depot only during those days and hours.  O. Reg. 298/94, s. 1.

50. Each operator and owner of a selected waste depot shall ensure that any selected waste accepted at the depot is deposited forthwith into storage containers at the depot.  O. Reg. 298/94, s. 1.

51. (1) Each operator and owner of a selected waste depot shall ensure that each person who accepts, handles, stores or deposits selected waste at the depot is knowledgeable about,

(a) legislation, regulations and Ministry guidelines relevant to the operation of the depot;

(b) environmental issues related to the selected waste to be handled at the depot;

(c) occupational health and safety issues related to the selected waste to be handled at the depot;

(d) the use and operation of any equipment likely to be used in the safe operation of the depot;

(e) procedures for dealing with emergencies, including fire and explosion, that might arise at the depot in connection with the selected waste to be handled there; and

(f) procedures for dealing with spills of selected waste at the depot, including clean-up, disposal and reporting procedures.  O. Reg. 298/94, s. 1.

(2) Each operator and owner of a selected waste depot shall ensure that each person who accepts, handles, stores or deposits selected waste at the depot is,

(a) an employee of the business associated with the depot;

(b) an owner of the business associated with the depot or a person who has the charge, management or control of the business associated with the depot; or

(c) an employee of a person mentioned in clause (b).  O. Reg. 298/94, s. 1.

52. (1) Each operator and owner of a selected waste depot shall take all reasonable steps to ensure that,

(a) selected waste is only accepted at the depot if it is of a type that results from the type of selected product regularly sold at the business associated with the depot;

(b) no more than five waste oil filters, no more than 25 litres of waste antifreeze and no more than 25 litres of waste lubricant are accepted at the depot from any one person on any one day; and

(c) selected waste is not accepted at the depot if it is brought to the depot by or on behalf of a generator required to submit a report under subsection 18 (1) in respect of the waste.  O. Reg. 298/94, s. 1.

(2) The taking of all reasonable steps for the purposes of subsection (1) includes ensuring that each person who accepts waste at the depot visually inspects waste before accepting it.  O. Reg. 298/94, s. 1.

53. Each operator and owner of a selected waste depot shall ensure that each type of selected waste stored at the depot is stored separate from each other type of selected waste, in storage containers and in accordance with the following rules:

1. Each storage container used to store selected waste shall bear a label or other identification that indicates the type of selected waste that it contains.

2. The label or other identification shall include the name and address of the depot.

3. In the case of an underground storage container, the label or other identification may be located on the fill pipe for the container and need not include the name and address of the depot.

4. The information required to be given on a label or other identification shall be set out so that it is clearly visible and legible.

5. Each storage container used to store selected waste shall be stored, handled and maintained so as to prevent leaks or spills of selected waste, damage or deterioration of the container, or any adverse effect.

6. Each storage container used to store selected waste shall be stored in a manner that facilitates the use of fire fighting equipment and spill containment and clean-up equipment throughout the depot and surrounding area.

7. Each storage container used to store selected waste shall be stored in a manner that facilitates inspection of the depot by a provincial officer.  O. Reg. 298/94, s. 1.

54. (1) Each operator and owner of a selected waste depot at which selected waste is stored in an above ground container shall ensure that the depot has a secondary containment system capable of containing leaks or spills of selected waste from the above ground container and capable of preventing the leaks or spills from entering municipal sewers, other drainage systems or the natural environment except air.  O. Reg. 298/94, s. 1.

(2) In the case of a selected waste depot at which selected waste is stored outdoors in an above ground container the base of which rests on the ground, each operator and owner shall also ensure that the secondary containment system is capable of draining leaks or spills away from the outdoor above ground container.  O. Reg. 298/94, s. 1.

55. (1) Each operator and owner of a selected waste depot shall ensure that the depot is equipped with fire fighting equipment and spill containment and clean-up equipment appropriate to the quantities and types of waste stored at the depot.  O. Reg. 298/94, s. 1.

(2) Each operator and owner of a selected waste depot shall ensure that the equipment mentioned in subsection (1) is stored in a way that makes it immediately accessible in the event that it is needed.  O. Reg. 298/94, s. 1.

56. (1) Each operator and owner of a selected waste depot shall ensure that the depot is visually inspected for leaks or spills of selected waste at least once during each day on which the business associated with the depot is open for sales or service.  O. Reg. 298/94, s. 1.

(2) Each operator and owner of a selected waste depot shall ensure that each inspection performed under subsection (1) on a day on which the depot is open to accept waste is performed by a person knowledgeable about the matters set out in clauses 51 (1) (a) to (f).  O. Reg. 298/94, s. 1.

(3) Each operator and owner of a selected waste depot shall ensure that at the time of each inspection under subsection (1) the person performing the inspection legibly records his or her name, the date and the findings of the inspection.  O. Reg. 298/94, s. 1.

(4) Each operator and owner of a selected waste depot shall ensure that each record made at the depot under subsection (1) is kept at the depot during a period of two years after it is made.  O. Reg. 298/94, s. 1.

57. (1) Each operator and owner of a selected waste depot shall ensure that each time selected waste is accepted at the depot, the person accepting the waste legibly records his or her name, the date, the name and address of the person who brought the waste to the depot and the type and approximate quantity of the waste.  O. Reg. 298/94, s. 1.

(2) Each operator and owner of a selected waste depot shall ensure that each record made at the depot under subsection (1) is kept at the depot during a period of two years after it is made.  O. Reg. 298/94, s. 1.

58. (1) Each operator and owner of a selected waste depot shall ensure that no selected waste is accepted at the depot unless there is in effect one or more written agreements each of which meets the requirements of subsections (2) and (3) and that together provide for the ongoing removal of all selected waste from the depot.  O. Reg. 298/94, s. 1.

(2) An agreement under subsection (1) shall be between an operator or owner of the depot and a party to whom a certificate of approval or provisional certificate of approval has been issued under Part V of the Act authorizing the party to transport one or more classes of waste that include the type or types of selected waste to be removed from the depot by the party under the agreement.  O. Reg. 298/94, s. 1.

(3) An agreement under subsection (1) shall state the following:

1. The name and address of an owner or operator of the depot.

2. The name and address of the party responsible for removing waste, the type of selected waste to be removed by the party and the number of the certificate of approval or provisional certificate of approval that authorizes the party to transport the type of waste.

3. The name, address and telephone number of an individual able to answer questions about the implementation of the agreement on behalf of the party responsible for removing the waste.

4. The approximate time intervals at which the party responsible for removing the waste will remove the waste.

5. The expiry date of the agreement.  O. Reg. 298/94, s. 1.

(4) Each operator and owner of a selected waste depot shall ensure that selected waste is removed from the depot only by a party to an agreement under subsection (1) to whom a certificate of approval or provisional certificate of approval has been issued authorizing the removal of the waste.  O. Reg. 298/94, s. 1.

(5) Each operator and owner of a selected waste depot shall ensure that a copy of an agreement under subsection (1) is kept at the depot during the term of the agreement and during a period of two years after the termination or expiry of the agreement.  O. Reg. 298/94, s. 1.

59. (1) Each operator and owner of a selected waste depot shall ensure that all selected waste is removed from the depot no later than 90 days after the depot ceases to be open to accept selected waste.  O. Reg. 298/94, s. 1.

(2) Each operator and owner of a selected waste depot shall ensure that written notice is given to the Chief Fire Official appointed under subsection 1.1.8 of Ontario Regulation 388/97 (Fire Code) made under the Fire Protection and Prevention Act, 1997 and to the Regional Director responsible for the region in which the depot is located no later than 95 days after the depot ceases to be open to accept selected waste.  O. Reg. 298/94, s. 1; O. Reg. 461/05, s. 12.

(3) The notice under subsection (2) shall include the following information:

1. The address of the depot and the location of the depot at the address.

2. The date on which the depot ceased being open to accept selected waste.

3. A statement that all selected waste has been removed from the depot.  O. Reg. 298/94, s. 1.

(4) Each operator and owner of a selected waste depot shall ensure that any documents required under sections 56 to 58 to be kept at the depot on the date referred to in paragraph 2 of subsection (3) are available to provincial officers for inspection at an address in Ontario during a period of two years after that date.  O. Reg. 298/94, s. 1.

(5) Each operator and owner of a selected waste depot shall ensure that the Chief Fire Official and the Regional Director responsible for the region in which the depot is located are given timely written notice of the address referred to in subsection (4).  O. Reg. 298/94, s. 1.

60. In the event of conflict between sections 44 to 59 of this Regulation and Ontario Regulation 388/97 (Fire Code) made under the Fire Protection and Prevention Act, 1997 or Ontario Regulation 213/01 (Fuel Oil) made under the Technical Standards and Safety Act, 2000, Ontario Regulation 388/97 or 213/01 prevails.  O. Reg. 461/05, s. 13.

Pesticide Container Depots

61. In this section and in sections 62 to 73,

“empty pesticide container” means an empty container originally used to hold commercial pesticides;

“pesticide” means any organism, substance or thing that is manufactured, represented, sold or used as a means of directly or indirectly controlling, preventing, destroying, mitigating, attracting or repelling any pest or of altering the growth, development or characteristics of any plant life that is not a pest and includes any organism, substance or thing registered under the Pest Control Products Act (Canada).  O. Reg. 298/94, s. 1.

62. (1) Sections 64 to 73 apply in relation to pesticide container depots that have the following characteristics:

1. The depot is at the place of business of a retail vendor licensed as such under the Pesticides Act.

2. The depot is managed by a person who owns or has the charge, management or control of the retail vendor business.

3. The depot is set up to accept, handle and store only empty pesticide containers.

4. The depot only accepts and stores empty pesticide containers that have been triple or jet rinsed and that do not exceed 23 litres in size if made of plastic or 20 litres in size if made of metal.  O. Reg. 298/94, s. 1.

(2) For the purposes of sections 64 to 73, a retail vendor business and a pesticide container depot are associated if they have the relationship to each other set out in paragraphs 1, 2 and 3 of subsection (1).  O. Reg. 298/94, s. 1.

63. (1) Sections 27, 40 and 41 of the Act do not apply in relation to a pesticide container depot that has the characteristics set out in subsection 62 (1).  O. Reg. 298/94, s. 1.

(2) Sections 27 and 41 of the Act and section 16 of this Regulation do not apply to the transportation of empty pesticide containers by the generator of the waste to a pesticide container depot that has the characteristics set out in subsection 62 (1).  O. Reg. 298/94, s. 1.

64. (1) Each owner and operator of a pesticide container depot shall ensure that no empty pesticide container is accepted at a pesticide container depot until 15 days after written notice of intent to operate the depot is given to the Regional Director responsible for the region in which the pesticide container depot is located.  O. Reg. 298/94, s. 1.

(2) The notice of intent to operate a pesticide container depot shall include the following information:

1. The address of the pesticide container depot and the location of the pesticide collection depot at that address.

2. The name under which the retail vendor business associated with the pesticide container depot carries on business.

3. The vendor licence number or operator licence number given under the Pesticides Act.

4. The name of the person who owns or has charge, management or control of the retail vendor business.  O. Reg. 298/94, s. 1.

(3) Each operator and owner of a pesticide container depot shall notify in writing the Regional Director responsible for the region in which the pesticide container depot is located of any change in respect of the information submitted under this section, no later than 15 days before the change occurs.  O. Reg. 298/94, s. 1.

65. Each operator and owner of a pesticide container depot shall ensure, by means of gates, fencing, locks, guards or otherwise, that only people authorized by an operator or owner have access to the empty pesticide containers at the pesticide container depot.  O. Reg. 298/94, s. 1.

66. Each operator and owner of a pesticide container depot shall ensure that notice of the days and hours during which empty pesticide containers will be accepted at the depot is clearly posted at the depot and shall ensure that empty pesticide containers are accepted at the depot only during those days and hours.  O. Reg. 298/94, s. 1.

67. Each operator and owner of a pesticide container depot shall ensure that any empty pesticide containers accepted at the depot are deposited immediately into a storage area at the pesticide container depot.  O. Reg. 298/94, s. 1.

68. (1) Each operator and owner of a pesticide container depot shall ensure that each person who accepts, handles, stores or deposits empty pesticide containers at the depot is knowledgeable about,

(a) legislation, regulations and Ministry guidelines relevant to the operation of the depot;

(b) environmental issues related to the empty pesticide containers to be handled at the depot;

(c) occupational health and safety issues related to the empty pesticide containers to be handled at the depot;

(d) the use and operation of any equipment likely to be used in the safe operation of the depot;

(e) procedures for dealing with emergencies, including fire and explosion, that might arise at the depot in connection with the empty pesticide containers to be handled there; and

(f) procedures for dealing with spills relating to the empty pesticide containers at the depot, including clean-up, disposal and reporting procedures.  O. Reg. 298/94, s. 1.

(2) Each operator and owner of a pesticide container depot shall ensure that each person who accepts, handles, stores or deposits empty pesticide containers at the depot is,

(a) an employee of the business associated with the depot;

(b) an owner of the business associated with the depot or a person who has the charge, management or control of the business associated with the depot; or

(c) an employee of a person mentioned in clause (b).  O. Reg. 298/94, s. 1.

69. Each operator and owner of a pesticide container depot shall take all reasonable steps to ensure that each person who accepts empty pesticide containers at the depot visually inspects the empty pesticide containers before accepting them for handling and storage.  O. Reg. 298/94, s. 1.

70. Each operator and owner of a pesticide container depot shall ensure that empty pesticide containers stored at the depot are stored in containers or areas in accordance with the following rules:

1. Each container or area used to store empty pesticide containers shall bear a label or other identification that indicates empty pesticide containers are stored within the container or area.

2. The information on the label or other identification shall be clearly visible and legible.

3. Each container used to store empty pesticide containers shall be stored, handled and maintained so as to prevent damage or deterioration of the containers, or any adverse effect.

4. Each container or area used to store empty pesticide containers shall be covered in such a manner so as to prevent rain water infiltration into or on the empty pesticide containers.

5. Each container used to store empty pesticide containers shall be stored in a manner that facilitates the use of fire fighting equipment and spill containment and clean-up equipment throughout the depot and surrounding area.

6. Each container used to store empty pesticide containers shall be stored in a manner that facilitates inspection of the depot by a provincial officer.

7. Each container or area used to store empty pesticide containers shall have ventilation to the outside atmosphere.  O. Reg. 298/94, s. 1.

71. Each operator and owner of a pesticide container depot shall ensure that records are kept of the type and quantity of empty pesticide containers accepted at the pesticide container depot.  O. Reg. 298/94, s. 1.

72. (1) Each operator and owner of a pesticide container depot shall ensure that no empty pesticide containers are accepted at the depot unless there is in effect one or more written agreements each of which meets the requirements of subsections (2) and (3) and that together provide for the ongoing removal of all empty pesticide containers from the depot.  O. Reg. 298/94, s. 1.

(2) An agreement under subsection (1) shall be between an operator or owner of the depot and a party to whom a certificate of approval or provisional certificate of approval has been issued under Part V of the Act authorizing the party to transport the empty pesticide containers to be removed from the depot.  O. Reg. 298/94, s. 1.

(3) The agreement shall state the following:

1. The name and address of the owner or operator of the pesticide container depot.

2. The name and address of the party responsible for removing the empty pesticide containers and the number of the certificate of approval or provisional certificate of approval that authorizes the party to transport them.

3. The name, address and telephone number of an individual able to answer questions about the implementation of the agreement on behalf of the party responsible for removing the empty pesticide containers.

4. The approximate time intervals at which the party responsible for removing the waste will remove the waste.

5. The expiry date of the agreement.  O. Reg. 298/94, s. 1.

(4) Each operator and owner of a pesticide container depot shall ensure that the empty pesticide containers are removed from the depot only by a party to an agreement under subsection (1) to whom a certificate of approval or provisional certificate of approval has been issued authorizing the removal of the waste.  O. Reg. 298/94, s. 1.

(5) Each operator and owner of a pesticide container depot shall ensure that a copy of the agreement is kept at the depot during the term of the agreement and for two years after the termination or expiration of the agreement.  O. Reg. 298/94, s. 1.

73. (1) Each operator and owner of a pesticide container depot shall ensure that all empty pesticide containers are removed from the depot no later than 90 days after the depot ceases to operate as a pesticide container depot.  O. Reg. 298/94, s. 1.

(2) Each operator and owner of a pesticide container depot shall ensure that written notice is given to the Regional Director responsible for the region in which the depot is located no later than 95 days after the depot ceases to be open to accept empty pesticide containers.  O. Reg. 298/94, s. 1.

(3) The notice under subsection (2) shall include the following information:

1. The address of the depot and the location of the depot at the address.

2. The date on which the depot ceased to operate as a pesticide container depot.

3. A statement that all empty pesticide containers have been removed from the pesticide container depot.  O. Reg. 298/94, s. 1.

(4) Each operator and owner of a pesticide container depot shall ensure that any documents required under sections 71 and 72 are kept at the depot and are available to provincial officers for inspection at an address in Ontario during a period of two years after the date on which the depot ceased to operate as a pesticide container depot.  O. Reg. 298/94, s. 1.

(5) Each operator and owner of a pesticide container depot shall ensure that the Regional Director responsible for the region in which the depot is located is given timely written notice of the address referred to in subsection (4).  O. Reg. 298/94, s. 1.

Land Disposal of Hazardous Waste

74. No person shall dispose of PCB waste by land disposal.  O. Reg. 461/05, s. 14.

Note:  On August 31, 2007, the Regulation is amended by adding the following sections:

75. (1) No person shall dispose of hazardous waste that is hazardous industrial waste by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules:

1. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 1 if the waste is an aqueous waste:

i. If Column 5 of Schedule 1 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Schedule 1 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 5 of Schedule 1 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

2. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 1 if the waste is a non-aqueous waste:

i. If Column 6 of Schedule 1 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Schedule 1 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 6 of Schedule 1 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. For the purpose of subparagraph ii, if the numerical concentration set out in Column 6 of Schedule 1 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure.

iv. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

3. If treatment subcategories are set out for the waste in Schedule 1, paragraphs 1 and 2 apply to the treatment subcategory that most closely describes the waste.  O. Reg. 461/05, s. 15.

(2) Dilution may not be used to comply with subparagraph 1 ii or 2 ii of subsection (1).  O. Reg. 461/05, s. 15.

(3) Despite subsection (1), a person may dispose of hazardous waste that is hazardous industrial waste by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1).  O. Reg. 461/05, s. 15.

(4) Subsections (1) to (3) do not apply to a waste until December 31, 2009 unless the waste is listed in Schedule 10.  O. Reg. 461/05, s. 15.

76. (1) No person shall dispose of hazardous waste that is acute hazardous waste chemical by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules:

1. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part A of Schedule 2 if the waste is an aqueous waste:

i. If Column 6 of Part A of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Part A of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 6 of Part A of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

2. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part A of Schedule 2 if the waste is a non-aqueous waste:

i. If Column 7 of Part A of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Part A of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 7 of Part A of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. For the purpose of subparagraph ii, if the numerical concentration set out in Column 7 of Part A of Schedule 2 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure.

iv. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

3. If treatment subcategories are set out for the waste in Part A of Schedule 2, paragraphs 1 and 2 apply to the treatment subcategory that most closely describes the waste.  O. Reg. 461/05, s. 15.

(2) Dilution may not be used to comply with subparagraph 1 ii or 2 ii of subsection (1).  O. Reg. 461/05, s. 15.

(3) Despite subsection (1), a person may dispose of hazardous waste that is acute hazardous waste chemical by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1).  O. Reg. 461/05, s. 15.

(4) Subsections (1) to (3) do not apply to a waste until December 31, 2009 unless the waste is listed in Schedule 11.  O. Reg. 461/05, s. 15.

77. (1) No person shall dispose of hazardous waste that is hazardous waste chemical by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules:

1. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part B of Schedule 2 if the waste is an aqueous waste:

i. If Column 6 of Part B of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Part B of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 6 of Part B of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

2. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part B of Schedule 2 if the waste is a non-aqueous waste:

i. If Column 7 of Part B of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Part B of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 7 of Part B of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. For the purpose of subparagraph ii, if the numerical concentration set out in Column 7 of Part B of Schedule 2 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure.

iv. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

3. If treatment subcategories are set out for the waste in Part B of Schedule 2, paragraphs 1 and 2 apply to the treatment subcategory that most closely describes the waste.  O. Reg. 461/05, s. 15.

(2) Dilution may not be used to comply with subparagraph 1 ii or 2 ii of subsection (1).  O. Reg. 461/05, s. 15.

(3) Despite subsection (1), a person may dispose of hazardous waste that is hazardous waste chemical by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1).  O. Reg. 461/05, s. 15.

(4) Subsections (1) to (3) do not apply to a waste until December 31, 2009 unless the waste is listed in Schedule 12.  O. Reg. 461/05, s. 15.

See:  O. Reg. 461/05, ss. 15, 29 (4).

Note:  On December 31, 2009, the Regulation is amended by adding the following section:

78. (1) No person shall dispose of hazardous waste that is severely toxic waste by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules:

1. If the waste is an aqueous waste, the waste must be treated so that, in the treated waste, based on an analysis of composite samples, the concentration of the regulated constituent set out for the waste in Schedule 3 is less than the numerical concentration set out for that regulated constituent in Column 6 of Schedule 3.

2. If the waste is a non-aqueous waste, the waste must be treated so that, in the treated waste, based on an analysis of grab samples, the concentration of the regulated constituent set out for the waste in Schedule 3 is less than the numerical concentration set out for that regulated constituent in Column 7 of Schedule 3.  O. Reg. 461/05, s. 16.

(2) Dilution may not be used to comply with paragraph 1 or 2 of subsection (1).  O. Reg. 461/05, s. 16.

(3) Despite subsection (1), a person may dispose of hazardous waste that is severely toxic waste by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1).  O. Reg. 461/05, s. 16.

See:  O. Reg. 461/05, ss. 16, 29 (5).

Note:  On August 31, 2007, the Regulation is amended by adding the following section:

79. (1) No person shall dispose of characteristic waste by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules:

1. Subject to paragraphs 3 and 4, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 5 if the waste is an aqueous waste:

i. If Column 5 of Schedule 5 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Schedule 5 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 5 of Schedule 5 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

iv. If Column 5 of Schedule 5 contains the words “meet Schedule 6 standards” in respect of a land disposal treatment requirement for the waste and, on or after December 31, 2009, the waste is treated in accordance with that requirement, the waste must also be treated so that, based on an analysis of composite samples, the concentration in the treated waste of each regulated constituent listed in Schedule 6 is less than the concentration set out for that regulated constituent in Column 3 of Schedule 6.

2. Subject to paragraphs 3 and 4, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 5 if the waste is a non-aqueous waste:

i. If Column 6 of Schedule 5 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Schedule 5 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 6 of Schedule 5 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

iv. If Column 6 of Schedule 5 contains the words “meet Schedule 6 standards” in respect of a land disposal treatment requirement for the waste and, on or after December 31, 2009, the waste is treated in accordance with that requirement, the waste must also be treated so that, based on an analysis of grab samples, the concentration in the treated waste of each regulated constituent listed in Schedule 6 is less than the concentration set out for that regulated constituent in Column 4 of Schedule 6.

v. For the purpose of subparagraphs ii and iv, if the numerical concentration set out in Column 6 of Schedule 5 or Column 4 of Schedule 6 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure.

3. If Column 5 or 6 of Schedule 5 contains the words “best efforts to achieve” in respect of a numerical concentration that is set out as the land disposal treatment requirement for that regulated constituent of the waste, it is not necessary for the concentration of the regulated constituent in the treated waste to be less than that concentration, but the person treating the waste must use the person’s best efforts to achieve that standard.

4. If treatment subcategories are set out for the waste in Schedule 5, paragraphs 1 to 3 apply to the treatment subcategory that most closely describes the waste.  O. Reg. 461/05, s. 17.

(2) Dilution may not be used to comply with subparagraph 1 ii or iv or 2 ii or iv of subsection (1).  O. Reg. 461/05, s. 17.

(3) Nothing in this section requires further treatment for a regulated constituent of a waste if,

(a) treatment that is required for the waste by subsection (1) causes the concentration of the regulated constituent in the treated waste to increase;

(b) a numerical concentration is set out as the land disposal treatment requirement for that regulated constituent of the waste in,

(i) Column 5 of Schedule 5, if the waste is an aqueous waste, or

(ii) Column 6 of Schedule 5, if the waste is a non-aqueous waste; and

(c) the concentration of the regulated constituent in the untreated waste was less than the concentration referred to in clause (b).  O. Reg. 461/05, s. 17.

(4) For the purpose of subsection (3), if the numerical concentration referred to in clause (3) (b) is expressed as a TCLP concentration, the concentration of the regulated constituent in the untreated waste and in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure.  O. Reg. 461/05, s. 17.

(5) Despite subsection (1), a person may dispose of characteristic waste by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1).  O. Reg. 461/05, s. 17.

(6) This section does not apply to a hazardous waste that is a characteristic waste and that is also a listed waste if all of the regulated constituents set out for the waste in Schedule 5 are regulated constituents set out for the waste in Schedule 1, Part A of Schedule 2, Part B of Schedule 2 or Schedule 3.  O. Reg. 461/05, s. 17.

(7) Subsections (1) to (5) do not apply to a waste until December 31, 2009 unless the waste is listed in Schedule 13.  O. Reg. 461/05, s. 17.

See:  O. Reg. 461/05, ss. 17, 29 (4).

Note:  On August 31, 2007, the Regulation is amended by adding the following sections:

80. (1) Sections 75, 77 and 79 do not apply to the land disposal of a sealed container if,

(a) a certificate described in subsection (3) is affixed to the container;

(b) the container does not appear to be broken or leaking; and

(c) the seal does not appear to be broken or tampered with.  O. Reg. 461/05, s. 18.

(2) A generator who transfers a sealed container containing waste shall affix a certificate described in subsection (3) to the container if,

(a) all the waste in the container is hazardous industrial waste, hazardous waste chemical or characteristic waste;

(b) the waste in the container was produced at the generator’s waste generation facility;

(c) the waste generation facility produces a total of less than 100 kilograms of hazardous industrial waste, hazardous waste chemical and characteristic waste in any month;

(d) no waste in the container has been mixed, blended, bulked or in any other way intermingled with any other waste or material;

(e) the container and its seal comply with any requirements of the Manual; and

(f) the total weight of the container and its contents does not exceed 250 kilograms.  O. Reg. 461/05, s. 18.

(3) The certificate referred to in clause (1) (a) and subsection (2) must contain the following:

1. The name, address and telephone number of the generator.

2. A statement that, pursuant to subsection (1), sections 75, 77 and 79 do not apply to the land disposal of the sealed container, as long as,

i. the container does not appear to be broken or leaking, and

ii. the seal does not appear to be broken or tampered with.

3. A description of the contents of the container, including,

i. a statement that all the waste in the container is hazardous industrial waste, hazardous waste chemical or characteristic waste,

ii. a statement that no waste in the container has been mixed, blended, bulked or in any other way intermingled with any other waste or material, and

iii. a statement that the waste in the container was produced at the generator’s waste generation facility.

4. A statement that the waste generation facility produces a total of less than 100 kilograms of hazardous industrial waste, hazardous waste chemical and characteristic waste in any month.

5. A statement that the container and its seal comply with any requirements of the Manual.

6. A statement that the total weight of the container and its contents does not exceed 250 kilograms.  O. Reg. 461/05, s. 18.

81. Sections 75 to 79 do not apply to the land disposal of hazardous waste that is composed only of combined quantities of individual wastes described in one or more of clauses (n), (p), (q), (r), (s), (t) and (u) of the definition of “hazardous waste” in subsection 1 (1) if,

(a) each of the individual wastes was brought to and accepted by a waste disposal site that accepts that type of waste from the general public, handles and temporarily stores it, but does not process or dispose of it; and

(b) each of the individual wastes would be hazardous waste if it were produced by a commercial or industrial generator or if it were produced in a larger quantity.  O. Reg. 461/05, s. 18.

See:  O. Reg. 461/05, ss. 18, 29 (4).

Note:  On August 31, 2007, the Regulation is amended by adding the following sections:

82. (1) Despite sections 75 to 79, a person may dispose of listed waste or characteristic waste by land disposal if the waste is soil or a soil mixture and the waste is first treated in accordance with the following rules:

1. If the soil or soil mixture is corrosive waste, ignitable waste or reactive waste, it must be treated so that it ceases to be corrosive waste, ignitable waste or reactive waste, as the case may be.

2. For each regulated constituent listed in Schedule 6 that can reasonably be expected to be present in the soil or soil mixture at a concentration that exceeds 10 times the standard set out for that regulated constituent in Column 4 of that Schedule, the soil or soil mixture must be treated so that,

i. the concentration of the regulated constituent after the treatment is not more than 10 per cent of the concentration of the regulated constituent before the treatment, or

ii. the concentration of the regulated constituent after the treatment is not more than 10 times the standard set out for the regulated constituent in Column 4 of Schedule 6.

3. For the purpose of subparagraph 2 i, the concentration of the regulated constituent shall be based on,

i. the total concentration of the regulated constituent in the soil or soil mixture, measured in milligrams per kilogram, if,

A. the regulated constituent is a metal, and the soil or soil mixture is treated using a metals removal technology,

B. the regulated constituent is carbon disulfide, cyclohexanone or methanol, and the soil or soil mixture is treated using a metals removal technology, or

C. the regulated constituent is not a metal and is not carbon disulfide, cyclohexanone or methanol, or

ii. if subparagraph i does not apply, the concentration of the regulated constituent in leachate from the treated media, measured in milligrams per litre, when the soil or soil mixture is tested using the Toxicity Characteristic Leaching Procedure.

4. If soil or a soil mixture is treated in accordance with paragraphs 1 to 3 and the residuals from the treatment are characteristic waste that is soil or a soil mixture, paragraphs 1 to 3 also apply to those residuals.  O. Reg. 461/05, s. 19.

(2) If soil or a soil mixture is treated in accordance with paragraphs 1 to 3 of subsection (1) and the residuals from the treatment are characteristic waste that is not soil or a soil mixture, section 79 applies to those residuals.  O. Reg. 461/05, s. 19.

83. (1) In this section,

“debris” means solid waste that has a particle size of more than 60 millimetres, and includes material that remains with debris when simple mechanical means or simple physical means are used to separate material that is debris from material that is not debris;

“debris mixture” means a mixture of debris and other material where, based on visual inspection, the volume of the mixture is made up primarily of debris.  O. Reg. 461/05, s. 19.

(2) Despite sections 75 to 79, a person may dispose of a listed waste or a characteristic waste by land disposal if the waste is debris or a debris mixture and the waste is first treated in accordance with the following rules:

1. One or more of the treatment methods listed in Schedule 8 must be used.

2. If Schedule 8 sets out restrictions applicable to a treatment method, that method may be used only in accordance with those restrictions.

3. When a treatment method listed in Schedule 8 is used, the treatment must achieve the standard set out for that treatment method in that Schedule.

4. If more than one treatment method listed in Schedule 8 is used and one of the treatment methods uses an immobilization technology, the method that uses the immobilization technology must be the last treatment method to be used.

5. After the waste is treated, the residuals from the treatment must be separated by simple mechanical means or simple physical means into,

i. residuals that are debris, and

ii. residuals that are not debris.

6. After the waste is treated, the residuals from the treatment that are debris must not be,

i. corrosive waste,

ii. ignitable waste,

iii. leachate toxic waste, or

iv. reactive waste.

7. If waste that is reactive waste because of the presence of cyanide is treated, the residuals from the treatment that are debris must be treated so that they may be land disposed in accordance with section 79 and, for that purpose, the residuals shall be deemed to be waste that is reactive waste because of the presence of cyanide.

8. If waste is treated by spalling, layers of the waste that are removed by spalling must be treated in accordance with the rules set out in this subsection and, for that purpose, the removed layers shall be deemed to be debris.

9. After the waste is treated, residuals from the treatment that are not debris must be treated in accordance with the following rules:

i. Residuals that are hazardous waste and are hazardous industrial waste must be treated so that they may be land disposed in accordance with section 75.

ii. Residuals that are hazardous waste and are acute hazardous waste chemical must be treated so that they may be land disposed in accordance with section 76.

iii. Residuals that are hazardous waste and are hazardous waste chemical must be treated so that they may be land disposed in accordance with section 77.

iv. Residuals that are hazardous waste and are severely toxic waste chemical must be treated so that they may be land disposed in accordance with section 78.

v. Residuals that are hazardous waste and are leachate toxic waste must be treated so that they may be land disposed in accordance with section 79.

vi. Residuals that are hazardous waste and are corrosive waste, ignitable waste or reactive waste must be treated so that they are no longer corrosive waste, ignitable waste or reactive waste, unless subparagraph vii applies.

vii. The following residuals from the treatment must be treated so that they may be land disposed in accordance with section 79 if they are hazardous waste:

A. Residuals that are reactive waste because of the presence of cyanide.

B. Residuals that are ignitable waste, are non-aqueous waste and contain 10 per cent total organic carbon or more.  O. Reg. 461/05, s. 19.

(3) If debris or a debris mixture is treated in accordance with the rules set out in subsection (2) and an immobilization technology described in Schedule 8 was not used, residuals from the treatment that are debris shall be deemed, for the purposes of this Regulation, not to be listed waste.  O. Reg. 461/05, s. 19.

(4) Subsection (2) does not apply to debris or a debris mixture that includes any of the following:

1. Lead acid batteries, cadmium batteries or radioactive lead solids.

2. Process residuals, including,

i. smelter slag,

ii. residues from the treatment of wastewater or other waste,

iii. sludge and residues from the treatment of sludge, and

iv. residues from air pollution control equipment.

3. Intact containers of hazardous waste that are not ruptured and that retain at least 75 per cent of the volume of the original container.  O. Reg. 461/05, s. 19.

See:  O. Reg. 461/05, ss. 19, 29 (4).

Note:  On August 31, 2007, the Regulation is amended by adding the following section:

84. (1) A generator who transfers any of the following waste to a receiving facility shall, before or at the time the waste is received at the receiving facility, give the receiver notice of the information referred to in subsection (2):

1. Characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed.

2. Waste that was characteristic waste but has been treated so that it is no longer characteristic waste, if the waste may not be disposed of by land disposal under subsection 79 (1).  O. Reg. 461/05, s. 20.

(2) The information referred to in subsection (1) is the current information relating to the waste that is contained in,

(a) the most recent annual Generator Registration Report submitted by the generator or, if no annual Generator Registration Report has been submitted, the initial Generator Registration Report submitted by the generator; and

(b) any subsequent supplementary Generator Registration Reports submitted by the generator.  O. Reg. 461/05, s. 20.

(3) The generator shall comply with subsection (1) by giving the information, or a specific Internet address where the information can be found,

(a) to the carrier who transports the waste to the receiving facility, with instructions to deliver it to the receiver when the waste is delivered;

(b) to the receiver, in accordance with section 182 of the Act; or

(c) to the receiver, by fax or another form of delivery.  O. Reg. 461/05, s. 20.

(4) The generator is only required to comply with subsection (1) in respect of,

(a) the first transfer to the receiving facility of each type of characteristic waste or listed waste identified in,

(i) the most recent annual Generator Registration Report submitted by the generator or, if no annual Generator Registration Report has been submitted, the initial Generator Registration Report submitted by the generator, and

(ii) any subsequent supplementary Generator Registration Reports submitted by the generator; and

(b) the first transfer to the receiving facility of a type of waste referred to in clause (a) following each significant change to information previously given to the receiver under subsection (1), if the change relates to the description or physical or chemical properties of that type of waste.  O. Reg. 461/05, s. 20.

(5) The generator shall make a record of its compliance with subsection (1), including the receiver to whom information was given under subsection (1) and the date the information was given.  O. Reg. 461/05, s. 20.

(6) The generator shall keep every record made under subsection (5) at the waste generation facility for two years.  O. Reg. 461/05, s. 20.

(7) If waste is transferred by a generator to a receiving facility, the waste was characteristic waste and the waste can be disposed of by land disposal under section 79,

(a) the generator shall, before or at the time the waste is received at the receiving facility, give the receiver notice that the waste was characteristic waste and that the waste can be disposed of by land disposal under section 79; and

(b) subsections (3) to (6) apply, with necessary modifications, in respect of a notice required by clause (a).  O. Reg. 461/05, s. 20.

See:  O. Reg. 461/05, ss. 20, 29 (4).

Note:  On August 31, 2007, the Regulation is amended by adding the following section:

85. (1) A generator or operator of a waste disposal site who treats waste in accordance with section 75, 76, 77, 78, 79, 82 or 83 shall develop and follow a written plan that requires regular and detailed chemical and physical testing of representative samples of the waste.  O. Reg. 461/05, s. 21.

(2) The person who develops the plan shall ensure that,

(a) the plan includes requirements to ensure that the testing will provide all information necessary to treat the waste in accordance with section 75, 76, 77, 78, 79, 82 or 83, as the case may be;

(b) the plan specifies the frequency with which testing will be conducted.  O. Reg. 461/05, s. 21.

(3) A person who develops a plan under subsection (1) shall keep a copy of the plan while that subsection applies to the person and for at least two years after that subsection ceases to apply to the person.  O. Reg. 461/05, s. 21.

(4) A person who is required to keep a copy of a plan under subsection (3) shall keep it at,

(a) the waste generation facility, if the person is a generator, or

(b) the waste disposal site, if the person is the operator of a waste disposal site.  O. Reg. 461/05, s. 21.

(5) The person who is required to follow a plan under subsection (1) shall make a record of the result of every test conducted in accordance with the plan.  O. Reg. 461/05, s. 21.

(6) A person who makes a record under subsection (5) shall keep the record for at least two years.  O. Reg. 461/05, s. 21.

See:  O. Reg. 461/05, ss. 21, 29 (4).

Form 1 Revoked:  O. Reg. 501/01, s. 12.

Form 2 Revoked:  O. Reg. 501/01, s. 12.

Schedule 1
HAZARDOUS INDUSTRIAL WASTES

Hazardous Industrial Waste from Non-Specific Sources

USEPA  Hazardous Waste No.

Industry and No.

Waste

F001

NA9301

The following spent halogenated solvents used in degreasing: Tetrachloroethylene, trichloroethylene, methylene chloride, 1,1,1-trichloroethane, carbon tetrachloride and chlorinated fluorocarbons; all spent solvent mixtures/blends used in degreasing containing, before use, a total of ten per cent or more (by volume) of one or more of the above halogenated solvents or those solvents listed in F002, F004 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

F002

NA9302

The following spent halogenated solvents: Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, chlorobenzene, 1,1,2-trichloro-1,2,2- trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane and 1,1,2-trichloro-ethane; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above halogenated solvents or those listed in F001, F004 or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

F003

NA9303

The following spent non-halogenated solvents: Xylene, acetone, ethyl acetate, ethyl benzene, ethyl ether, methyl isobutyl ketone, n-butyl alcohol, cyclohexanone and methanol; all spent solvent mixtures/blends containing, before use, only the above spent non-halogenated solvents; and all spent solvent mixtures/blends containing, before use, one or more of the above non-halogenated solvents, and, a total of ten per cent or more (by volume) of one or more of those solvents listed in F001, F002, F004 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

F004

NA9304

The following spent non-halogenated solvents: Cresols and cresylic acid, and nitrobenzene; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

F005

NA9305

The following spent non-halogenated solvents: Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, benzene, 2-ethoxyethanol, and 2-nitropropane; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002 or F004; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

F006

NA9306

Wastewater treatment sludges from electroplating operations except from the following processes: (1) Sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon steel; (5) cleaning/stripping associated with tin, zinc and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum.

F007

NA9308

Spent cyanide plating bath solutions from electroplating operations

F008

NA9309

Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process.

F009

NA9310

Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.

F010

NA9311

Quenching bath residues from oil baths from metal heat treating operations where cyanides are used in the process.

F011

NA9312

Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.

F012

NA9313

Quenching waste water treatment sludges from metal heat treating operations where cyanides are used in the process.

F019

NA9307

Wastewater treatment sludges from the chemical conversion coating of aluminum except from zirconium phosphating in aluminum can washing when such phosphating is an exclusive conversion coating process.

F020

 

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- or tetrachlorophenol, or of intermediates used to produce their pesticide derivatives. (This listing does not include wastes from the production of Hexachlorophene from highly purified 2,4,5- trichlorophenol.).

F021

 

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of pentachlorophenol, or of intermediates used to produce its derivatives.

F022

 

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tetra-, penta-, or hexachlorobenzenes under alkaline conditions.

F023

 

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- and tetrachlorophenols. (This listing does not include wastes from equipment used only for the production or use of Hexachlorophene from highly purified 2,4,5-trichlorophenol.).

F024

 

Process wastes, including but not limited to, distillation residues, heavy ends, tars, and reactor cleanout wastes, from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes.  These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. (This listing does not include wastewaters, wastewater treatment sludges, spent catalysts, and wastes listed in Schedules 2A or 2B.).

F025

 

Condensed light ends, spent filters and filter aids, and spent desiccant wastes from the production of certain chlorinated aliphatic hydrocarbons, by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution.

F026

 

Wastes (except wastewater and spent carbon rom hydrogen chloride purification) from the production of materials on equipment previously used for the manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tetra-, penta-, or hexachlorobenzene under alkaline conditions.

F027

 

Discarded unused formulations containing tri-, tetra-, or pentachlorophenol or discarded unused formulations containing compounds derived from these chlorophenols. (This listing does not include formulations containing Hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component.).

F028

 

Residues resulting from the incineration or thermal treatment of soil contaminated with EPA Hazardous Waste Nos. F020, F021, F022, F023, F026 and F027.

F032

 

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that currently use or have previously used chlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with s. 261.351 or potentially cross-contaminated wastes that are otherwise currently regulated as hazardous wastes (i.e., F034 or F035), and where the generator does not resume or initiate use of chlorophenolic formulations).  This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

F034

 

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use creosote formulations. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

F035

 

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use inorganic preservatives containing arsenic or chromium. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

F037

 

Petroleum refinery primary oil/water/solids separation sludge — Any sludge generated from the gravitational separation of oil/water/solids during the storage or treatment of process wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but are not limited to, those generated in: oil/water/solids separators; tanks and impoundments; ditches and other conveyances; sumps; and stormwater units receiving dry weather flow. Sludge generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges generated in aggressive biological treatment units as defined in s. 261.31(b)(2)1 (including sludges generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and K051 wastes are not included in this listing.  This listing does include residuals generated from processing or recycling oil-bearing hazardous secondary materials excluded under s. 261.4(a)(12)(i)1, if those residuals are to be disposed of.

F038

 

Petroleum refinery secondary (emulsified) oil/water/solids separation sludge — Any sludge and/or float generated from the physical and/or chemical separation of oil/ water/solids in process wastewaters and oily cooling wastewaters from petroleum refineries. Such wastes include, but are not limited to, all sludges and floats generated in: induced air flotation (IAF) units, tanks and impoundments, and all sludges generated in DAF units. Sludges generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges and floats generated in aggressive biological treatment units as defined in s. 261.31(b)(2)1 (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and F037, K048, and K051 wastes are not included in this listing.

F039

 

Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one restricted waste classified as hazardous under subpart D of this part. (Leachate resulting from the disposal of one or more of the following EPA Hazardous Wastes and no other Hazardous Wastes retains its EPA Hazardous Waste Number(s): F020, F021, F022, F026, F027, and/or F028.).

 

Hazardous Industrial Waste from Specific Sources

USEPA  HazardousWaste No.

Industry and No.

Waste

Wood preservation:

K001

NA9316

Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote and/or pentachlorophenol.

Inorganic pigments:

K002

NA9317

Wastewater treatment sludge from the production of chrome yellow and orange pigments.

K003

NA9318

Wastewater treatment sludge from the production of molybdate orange pigments.

K004

NA9319

Wastewater treatment sludge from the production of zinc yellow pigments.

K005

NA9320

Wastewater treatment sludge from the production of chrome green pigments.

K006

NA9321

Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated).

K007

NA9322

Wastewater treatment sludge from the production of iron blue pigments.

K008

NA9323

Oven residue from the production of chrome oxide green pigments.

Organic chemicals:

K009

NA9324

Distillation bottoms from the production of acetaldehyde from ethylene.

K010

NA9325

Distillation side cuts from the production of acetaldehyde from ethylene.

K011

NA9326

Bottom stream from the wastewater stripper in the production of acrylonitrile.

K013

NA9327

Bottom stream from the acetonitrile column in the production of acrylonitrile.

K014

NA9328

Bottoms from the acetonitrile purification column in the production of acrylonitrile.

K015

NA9329

Still bottoms from the distillation of benzyl chloride.

K016

NA9330

Heavy ends or distillation residues from the production of carbon tetrachloride.

K017

NA9331

Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.

K018

NA9332

Heavy ends from the fractionation column in ethyl chloride production.

K019

NA9333

Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.

K020

NA9334

Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.

K021

NA9335

Aqueous spent antimony catalyst waste from fluoromethanes production.

K022

NA9336

Distillation bottom tars from the production of phenol/acetone from cumene.

K023

NA9337

Distillation light ends from the production of phthalic anhydride from naphthalene.

K024

NA9338

Distillation bottoms from the production of phthalic anhydride from naphthalene.

K025

NA9341

Distillation bottoms from the production of nitrobenzene by the nitration of benzene.

K026

NA9342

Stripping still tails from the production of methyl ethyl pyridines.

K027

NA9343

Centrifuge and distillation residues from toluene diisocyanate production.

K028

NA9344

Spent catalyst from the hydrochlorinator reactor in the productions of 1,1,1trichloroethane.

K029

NA9345

Waste from the product stream stripper in the production of 1,1,1trichloroethane.

K030

NA9348

Column bottoms or heavy ends from the combined production of trichloroethylene and perchloroethylene.

K083

NA9349

Distillation bottoms from aniline production.

K085

NA9352

Distillation or fractionation column bottoms from the production of chlorobenzenes.

K093

NA9339

Distillation light ends from the production of phthalic anhydride from orthoxylene.

K094

NA9340

Distillation bottoms from the production of phthalic anhydride from orthoxylene.

K095

NA9346

Distillation bottoms from the production of 1,1,1trichloroethane.

K096

NA9347

Heavy ends from the heavy ends column from the production of 1,1,1trichloroethane.

K103

NA9350

Process residues from aniline extraction from the production of aniline.

K104

NA9351

Combined wastewater streams generated from nitrobenzene/aniline production.

K105

NA9353

Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes.

K107

 

Column bottoms from product separation from the production of 1,1-dimethyl-hydra-zine (UDMH) from carboxylic acid hydrazines.

K108

 

Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

K109

 

Spent filter cartridges from product purification from the production of 1,1- dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

K110

 

Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

K111

 

Product washwaters from the production of dinitrotoluene via nitration of toluene.

K112

 

Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene.

K113

 

Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

K114

 

Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

K115

 

Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

K116

 

Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.

K117

 

Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene.

K118

 

Spent adsorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.

K136

 

Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.

K140

 

Floor sweepings, off-specification product and spent filter media from the production of 2,4,6-tribromophenol.

K149

 

Distillation bottoms from the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.  (This waste does not include still bottoms from the distillation of benzyl chloride.)

K150

 

Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of alpha-( or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.

K151

 

Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.

K156

 

Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes.  (This listing does not apply to wastes generated from the manufacture of 3-iodo-2- propynyl n-butylcarbamate.).

K157

 

Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)

K158

 

Bag house dusts and filter/separation solids from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.).

K159

 

Organics from the treatment of thiocarbamate wastes.

K161

 

Purification solids (including filtration, evaporation, and centrifugation solids), bag house dust and floor sweepings from the production of dithiocarbamate acids and their salts. (This listing does not include K125 or K126.)

Inorganic chemicals:

K071

NA9390

Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used.

K073

NA9391

Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production.

K106

NA9392

Wastewater treatment sludge from the mercury cell process in chlorine production.

Pesticides:

K031

NA9354

Byproduct salts generated in the production of MSMA and cacodylic acid.

K032

NA9355

Wastewater treatment sludge from the production of chlordane.

K033

NA9356

Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane.

K034

NA9357

Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.

K035

NA9359

Wastewater treatment sludges generated in the production of creosote.

K036

NA9360

Still bottoms from toluene reclamation distillation in the production of disulphoton.

K037

NA9361

Wastewater treatment sludges from the production of disulphoton.

K038

NA9362

Wastewater from the washing and stripping of phorate production.

K039

NA9363

Filter cake from the filtration of diethyl phosphorodithioic acid in the production of phorate.

K040

NA9364

Wastewater treatment sludge from the production of phorate.

K041

NA9365

Wastewater treatment sludge from the production of toxaphene.

K042

NA9367

Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5T.

K043

NA9368

2,6Dichlorophenol waste from the production of 2,4D.

K097

NA9358

Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.

K098

NA9366

Untreated process wastewater from the production of toxaphene.

K099

NA9369

Untreated wastewater from the production of 2,4D.

K123

 

Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salt.

K124

 

Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.

K125

 

Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.

K126

 

Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.

K131

 

Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide.

K132

 

Spent absorbent and wastewater separator solids from the production of methyl bromide.

Explosives:

K044

NA9370

Wastewater treatment sludges from the manufacturing and processing of explosives.

K045

NA9371

Spent carbon from the treatment of wastewater containing explosives.

K046

NA9372

Wastewater treatment sludges from the manufacturing formulation and loading of leadbased initiating compounds.

K047

NA9373

Pink/red water from TNT operations.

Petroleum refining:

K048

NA9374

Dissolved air flotation (DAF) float from the petroleum refining industry.

K049

NA9375

Slop oil emulsion solids from the petroleum refining industry.

K050

NA9376

Heat exchanger bundle cleaning sludge from the petroleum refining industry.

K051

NA9377

API separator sludge from the petroleum refining industry.

K052

NA9378

Tank bottoms (leaded) from the petroleum refining industry.

K169

 

Crude oil storage tank sediment from petroleum refining operations.

K170

 

Clarified slurry oil tank sediment and/or in-line filter/separation solids from petroleum refining operations.

K171

 

Spent Hydrotreating catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media).

K172

 

Spent Hydrorefining catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media).

Iron and steel:

K061

NA9380

Emission control dust/sludge from the primary production of steel in electric furnaces.

K062

NA9381

Spent pickle liquor generated by steel finishing operations within the iron and steel industry at steel works, blast furnaces (including coke ovens), rolling mills, iron and steel foundries, gray and ductile iron foundries, malleable iron foundries, steel investment foundries or other miscellaneous steel foundries or at facilities in the electrometallurgical products (except steel) industry, steel wiredrawing and steel nails and spikes industry, cold-rolled steel sheet, strip and bars industry, or steel pipe and tubes industry.

Primary copper:

K064

NA9383

Acid plant blowdown slurry/sludge resulting from the thickening of blowdown slurry from primary copper production.

Primary lead:

K065

NA9384

Surface impoundment solids contained in and dredged from surface impoundments at primary lead smelting facilities.

Primary zinc:

K066

NA9385

Sludge from treatment of process wastewater and/or acid plant blowdown from primary zinc production.

Primary aluminum:

K088

 

Spent potliners from primary aluminum reduction.

Ferroalloys:

K090

 

Emission control dust or sludge from ferrochromiumsilicon production.

K091

 

Emission control dust or sludge from ferrochromium production.

Secondary lead:

K069

NA9388

Emission control dust/sludge from secondary lead smelting. (NOTE: This listing is stayed administratively for sludge generated from secondary acid scrubber systems.  The stay will remain in effect until further administrative action is taken. If EPA takes further action effecting this stay, EPA will publish a notice of the action in the Federal Register.

K100

NA9389

Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting.

Veterinary pharmaceuticals:

K084

NA9394

Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.

K101

NA9395

Distillation tar residues from the distillation of anilinebased compounds in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.

K102

NA9396

Residue from the use of activated carbon for decolourization in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.

Ink formulation:

K086

NA9393

Solvent washes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, driers, soaps, and stabilizers containing chromium and lead.

Coking:

K060

NA9379

Ammonia still lime sludge from coking operations.

K087

NA9397

Decanter tank tar sludge from coking operations.

K141

 

Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke from coal or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludges from coking operations).

K142

 

Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.

K143

 

Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal.

K144

 

Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal.

K145

 

Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.

K147

 

Tar storage tank residues from coal tar refining.

K148

 

Residues from coal tar distillation, including but not limited to, still bottoms.

1 Resource Conservation and Recovery Act (RCRA), United States Congress, 42 U.S.C. s/s 6901 et seq. (1976),

Subtitle C, Code of Federal Regulations, 40CFR, Chapter I – Environmental Protection Agency, Subchapter I – Solid Wastes, Part 261 – Identification and Listing of Hazardous Waste

O. Reg. 558/00, s. 4.

Note:  On January 1, 2007, Schedule 1 is revoked and the following substituted:

Schedule 1
Hazardous Industrial Waste

Hazardous Industrial Waste from Non-Specific Sources

Hazardous Industrial Waste

Regulated Constituents
(and Treatment Subcategories1)

Land Disposal Treatment Requirements

Aqueous Waste

Non-aqueous Waste

Column 1

Column 2

Column 3

Column 4

Column 5

Column 6

Haz. Waste Number2

Waste

Generic Name or other description

CAS Number3

Treatment Code4 or Concentration5 (mg/L)

Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated)

F001

The following spent halogenated solvents used in degreasing: Tetrachloroethylene, trichloroethylene, methylene chloride, 1,1,1-trichloroethane, carbon tetrachloride and chlorinated fluorocarbons; all spent solvent mixtures/blends used in degreasing containing, before use, a total of ten per cent or more (by volume) of one or more of the above halogenated solvents or those solvents listed in F002, F004 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

Acetone

67-64-1

0.28

160

Benzene

71-43-2

0.14

10

n-Buthyl alcohol

71-36-3

5.6

2.6

Carbon disulfide

75-15-0

3.8

NA

Carbon tetrachloride

56-23-5

0.057

6.0

Chlorobenzene

108-90-7

0.057

6.0

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p- cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m- cresol) 

106-44-5

0.77

5.6

Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations)

1319-77-3

0.88

11.2

Cyclohexanone

108-94-1

0.36

NA

o-Dichlorobenzene

95-50-1

0.088

6.0

Ethyl acetate

141-78-6

0.34

33

Ethyl benzene

100-41-4

0.057

10

Ethyl ether

60-29-7

0.12

160

Isobutyl alcohol

78-83-1

5.6

170

Methanol

67-56-1

5.6

NA

Methylene chloride

75-9-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Methyl isobutyl ketone

108-10-1

0.14

33

Nitrobenzene

98-95-3

0.068

14

Pyridine

110-86-1

0.014

16

Tetrachloroethylene

127-18-4

0.056

6.0

Toluene

108-88-3

0.08

10

1,1,1-Trichloroethane

71-55-6

0.054

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

1,1,2-Trichloro-1,2,2-trifluoroethane

76-13-1

0.057

30

Trichloroethylene

79-01-6

0.054

6.0

Trichlorofluoromethane

75-69-4

0.02

30

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

F002

The following spent halogenated solvents: Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, chlorobenzene, 1,1,2-trichloro-1,2,2- trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane and 1,1,2-trichloro-ethane; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above halogenated solvents or those listed in F001, F004 or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

same as F001

 

 

 

F003

The following spent non-halogenated solvents: Xylene, acetone, ethyl acetate, ethyl benzene, ethyl ether, methyl isobutyl ketone, n-butyl alcohol, cyclohexanone and methanol; all spent solvent mixtures/blends containing, before use, only the above spent non-halogenated solvents; and all spent solvent mixtures/blends containing, before use, one or more of the above non-halogenated solvents, and, a total of ten per cent or more (by volume) of one or more of those solvents listed in F001, F002, F004 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

Treatment Subcategory 1

All F003 wastes, except those identified in Subcategory 2:

same as F001

 

 

 

Treatment Subcategory 2

F003 solvent wastes, that contain any combination of one or more of the following three solvents as the only listed F001-5 solvents: carbon disulfide, cyclohexanone and/or methanol:

Carbon disulfide

75-15-0

3.8

4.8 mg/L TCLP

Cyclohexanone

108-94-1

0.36

0.75 mg/L TCLP

Methanol

67-56-1

5.6

0.75 mg/L TCLP

 

 

 

 

F004

The following spent non-halogenated solvents: Cresols and cresylic acid, and nitrobenzene; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

same as F001

 

 

 

F005

The following spent non-halogenated solvents: Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, benzene, 2-ethoxyethanol, and 2-nitropropane; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002 or F004; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

Treatment Subcategory 1

All F003 wastes, except those identified in Subcategory 2:

same as F001

 

 

 

Treatment Subcategory 2

F003 solvent wastes, that contain any combination of one or more of the following three solvents as the only listed F001-5 solvents: carbon disulfide, cyclohexanone and/or methanol:

same as F003 Subcategory 2

 

 

 

Treatment Subcategory 3

F005 solvent waste containing 2-Nitropropane as the only listed F001-5 solvents:

2-Nitropropane

79-46-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

Treatment Subcategory 4

F005 solvent waste containing 2-Ethoxyethanol as the only listed F001-5 solvents:

2-Ethoxyethanol

110-80-5

BIODG; or CMBST

CMBST

F006

Wastewater treatment sludges from electroplating operations except from the following processes: (1) Sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon steel; (5) cleaning/stripping associated with tin, zinc and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum.

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

 

 

 

 

F007

Spent cyanide plating bath solutions from electroplating operations.

Cadmium

7440-43-9

NA

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

F008

Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process.

Cadmium

7440-43-9

NA

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

F009

Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.

Cadmium

7440-43-9

NA

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

F010

Quenching bath residues from oil baths from metal heat treating operations where cyanides are used in the process.

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

NA

 

 

 

 

F011

Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.

Cadmium

7440-43-9

NA

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

F012

Quenching waste water treatment sludges from metal heat treating operations where cyanides are used in the process.

Cadmium

7440-43-9

NA

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

F019

Wastewater treatment sludges from the chemical conversion coating of aluminum except from zirconium phosphating in aluminum can washing when such phosphating is an exclusive conversion coating process.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

 

 

 

 

F020

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- or tetrachlorophenol, or of intermediates used to produce their pesticide derivatives. (This listing does not include wastes from the production of Hexachlorophene from highly purified 2,4,5- trichlorophenol.)

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

Hx CDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

Pentachlorophenol

87-86-5

0.089

7.4

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4-6-Trichlorophenol

88-06-2

0.035

7.4

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

F021

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of pentachlorophenol, or of intermediates used to produce its derivatives.

Same as F020

 

 

 

F022

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tetra-, penta-, or hexachlorobenzenes under alkaline conditions.

Same as F020

 

 

 

F023

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- and tetrachlorophenols. (This listing does not include wastes from equipment used only for the production or use of Hexachlorophene from highly purified 2,4,5-trichlorophenol.)

Same as F020

 

 

 

F024

Process wastes, including but not limited to, distillation residues, heavy ends, tars, and reactor cleanout wastes, from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. (This listing does not include wastewaters, wastewater treatment sludges, spent catalysts, and wastes listed in Part A or B of Schedule 2.)

All F024 wastes

NA

CMBST8

CMBST8

2-Chloro-1,3-butadiene

126-99-8

0.057

0.28

3-Chloropropylene

107-05-1

0.036

30

1,1-Dichloroethane

75-34-3

0.059

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

1,2-Dichloropropane

78-87-5

0.85

18

cis-1,3-Dichloropropylene

10061-01-5

0.036

18

trans-1-3-Dichloropropylene

10061-02-6

0.036

18

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Hexachloroethane

67-72-1

0.055

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

 

 

 

 

F025

Condensed light ends, spent filters and filter aids, and spent desiccant wastes from the production of certain chlorinated aliphatic hydrocarbons, by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution.

Treatment Subcategory 1

F025 Light Ends:

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

1,1-Dichloroethylene

75-35-4

0.025

6.0

Methylene chloride

75-9-2

0.089

30

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Vinyl chloride

75-01-4

0.027

6.0

Treatment Subcategory 2

F025 Spent Filters/Aids and Desiccants:

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Methylene chloride

75-9-2

0.089

30

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Vinyl chloride

75-01-4

0.27

6.0

F026

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tetra-, penta-, or hexachlorobenzene under alkaline conditions.

Same as F020

 

 

 

F027

Discarded unused formulations containing tri-, tetra-, or pentachlorophenol or discarded unused formulations containing compounds derived from these chlorophenols. (This listing does not include formulations containing Hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component.)

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

Pentachlorophenol

87-86-5

0.089

7.4

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

F028

Residues resulting from the incineration or thermal treatment of soil contaminated with Hazardous Waste Numbers F020, F021, F022, F023, F026 and F027.

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

Pentachlorophenol

87-86-5

0.089

7.4

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

F032

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that currently use or have previously used chlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with s. 261.359 or potentially cross-contaminated wastes that are otherwise currently regulated as hazardous wastes (i.e., F034 or F035), and where the generator does not resume or initiate use of chlorophenolic formulations). This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

Acenaphthene

83-32-9

0.059

3.4

Anthracene

120-12-7

0.059

3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Benzo(a)pyrene

50-32-8

0.061

3.4

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h) anthracene

53-70-3

0.055

8.2

2-4-Dimethyl phenol

105-67-9

0.036

14

Fluorene

86-73-7

0.059

3.4

Hexachlorodibenzo-p-dioxins

NA

0.000063 or CMBST8

0.001 or CMBST8

Hexachlorodibenzofurans

NA

0.000063 or CMBST8

0.001 or CMBST8

Indeno (1,2,3-c,d) pyrene

193-39-5

0.0055

3.4

Naphthalene

91-20-3

0.059

5.6

Pentachlorodibenzo-p-dioxins

NA

0.000063 or CMBST8

0.001 or CMBST8

Pentachlorodibenzofurans

NA

0.000035 or CMBST8

0.001 or CMBST8

Pentachlorophenol

87-86-5

0.089

7.4

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Tetrachlorodibenzo-p-dioxins

NA

0.000063 or CMBST8

0.001 or CMBST8

Tetrachlorodibenzofurans

NA

0.000063 or CMBST8

0.001 or CMBST8

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

F034

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use creosote formulations. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

Acenaphthene

83-32-9

0.059

3.4

Anthracene

120-12-7

0.059

3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Benzo(a)pyrene

50-32-8

0.061

3.4

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Fluorene

86-73-7

0.059

3.4

Indeno(1,2,3-c,d)pyrene

193-39-5

0.0055

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

F035

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use inorganic preservatives containing arsenic or chromium. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

 

 

 

 

F037

Petroleum refinery primary oil/water/solids separation sludge - Any sludge generated from the gravitational separation of oil/water/solids during the storage or treatment of process wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but are not limited to, those generated in: oil/water/solids separators; tanks and impoundments; ditches and other conveyances; sumps; and stormwater units receiving dry weather flow. Sludge generated in stormwater units that do not receive dry weather flow, sludges generated from non‑contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges generated in aggressive biological treatment units as defined in s. 261.31(b)(2)9 (including sludges generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and K051 wastes are not included in this listing. This listing does include residuals generated from processing or recycling oil-bearing hazardous secondary materials excluded under s.261.4(a)(12)(i)9, if those residuals are to be disposed of.

Acenaphthene

83-32-9

0.059

NA

Anthracene

120-12-7

0.059

3.4

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

Chrysene

218-01-9

0.059

3.4

Di-n-butyl phthalate

84-74-2

0.057

28

Ethylbenzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

NA

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

F038

Petroleum refinery secondary (emulsified) oil/water/solids separation sludge - Any sludge and/or float generated from the physical and/or chemical separation of oil/ water/solids in process wastewaters and oily cooling wastewaters from petroleum refineries. Such wastes include, but are not limited to, all sludges and floats generated in: induced air flotation (IAF) units, tanks and impoundments, and all sludges generated in DAF units. Sludges generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges and floats generated in aggressive biological treatment units as defined in s. 261.31(b)(2)9 (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and F037, K048, and K051 wastes are not included in this listing.

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

Chrysene

218-01-9

0.059

3.4

Di-n-butyl phthalate

84-74-2

0.057

28

Ethylbenzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

NA

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o, m-, and p- xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

 

 

 

 

F039

Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one hazardous waste. (Leachate resulting from the disposal of one or more of the following Hazardous Wastes and no other Hazardous Wastes retains its Hazardous Waste Number(s): F020, F021, F022, F026, F027, and/or F028.)

Acenaphthylene

208-96-8

0.059

3.4

Acenaphthene

83-32-9

0.059

3.4

Acetone

67-64-1

0.28

160

Acetonitrile

75-05-8

5.6

NA

Acetophenone

96-86-2

0.01

9.7

2-Acetylaminofluorene

53-96-3

0.059

140

Acrolein

107-02-8

0.29

NA

Acrylonitrile

107-13-1

0.24

84

Aldrin

309-00-2

0.021

0.066

4-Aminobiphenyl

92-67-1

0.13

NA

Aniline

62-53-3

0.81

14

Anthracene

120-12-7

0.059

3.4

Aramite

140-57-8

0.36

NA

alpha-BHC

319-84-6

0.00014

0.066

beta-BHC

319-85-7

0.00014

0.066

delta-BHC

319-86-8

0.023

0.066

gamma-BHC

58-89-9

0.0017

0.066

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Benzo(a)pyrene

50-32-8

0.061

3.4

Bromodichloromethane

75-27-4

0.35

15

Methyl bromide (Bromomethane)

74-83-9

0.11

15

4-Bromophenyl phenyl ether

101-55-3

0.055

15

n-Butyl alcohol

71-36-3

5.6

2.6

Butyl benzyl phthalate

85-68-7

0.017

28

2-sec-Buty-4,6-dinitrophenol (Dinoseb)

88-85-7

0.066

2.5

Carbon disulfide

75-15-0

3.8

NA

Carbon tetrachloride

56-23-5

0.057

6.0

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

p-Chloroaniline

106-47-8

0.46

16

Chlorobenzene

108-90-7

0.057

6.0

Chlorobenzilate

510-15-6

0.1

NA

2-Chloro-1,3-butadiene

126-99-8

0.057

NA

Chlorodibromomethane

124-48-1

0.057

15

Chloroethane

75-00-3

0.27

6

bis(2-Chloroethoxy)methane

111-91-1

0.036

7.2

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

Chloroform

67-66-3

0.046

6.0

bis(2-Chloroisopropyl)ether

39638-32-9

0.055

7.2

p-Chloro-m-cresol

59-50-7

0.018

14

Chloromethane (Methyl chloride)

74-87-3

0.19

30

2-Chloronaphthalene

91-58-7

0.055

5.6

2-Chlorophenol

95-57-8

0.044

5.7

3-Chloropropylene

107-05-1

0.036

30

Chrysene

218-01-9

0.059

3.4

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p- cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m- cresol)

106-44-5

0.77

5.6

Cyclohexanone

108-94-1

0.36

NA

1,2-Dibromo-3-chloropropane

96-12-8

0.11

15

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

Dibromomethane

74-95-3

0.11

15

2,4-D (2,4-Dichlorophenoxyacetic acid)

94-75-7

0.72

10

o,p'-DD

53-19-0

0.023

0.087

p,p'-DDD

72-54-8

0.023

0.087

o,p'-DDE

3424-82-6

0.031

0.087

p,p'-DDE

72-55-9

0.031

0.087

o,p'-DDT

789-02-6

0.0039

0.087

p,p'-DDT

50-29-3

0.0039

0.087

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Dibenz(a,e)pyrene

192-65-4

0.061

NA

m-Dichlorobenzene

541-73-1

0.036

6.0

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.09

6.0

Dichlorodifluoromethane

75-71-8

0.23

7.2

1,1-Dichloroethane

75-34-3

0.059

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

1,1-Dichloroethylene

75-35-4

0.025

6.0

trans-1,2-Dichloroethylene

156-60-5

0.054

30

2,4-Dichlorophenol

120-83-2

0.044

14

2,6-Dichlorophenol

87-65-0

0.044

14

1,2-Dichloropropane

78-87-5

0.85

18

cis-1,3-Dichloropropylene

10061-01-5

0.036

18

trans-1,3-Dichloropropylene

10061-02-6

0.036

18

Dieldrin

60-57-1

0.017

0.13

Diethyl phthalate

84-66-2

0.2

28

2-4-Dimethyl phenol

105-67-9

0.036

14

Dimethyl phthalate

131-11-3

0.047

28

Di-n-butyl phthalate

84-74-2

0.057

28

1,4-Dinitrobenzene

100-25-4

0.32

2.3

4,6-Dinitro-o-cresol

534-52-1

0.28

160

2,4-Dinitrophenol

51-28-5

0.12

160

2,4-Dinitrotoluene

121-14-2

0.32

140

2,6-Dinitrotoluene

606-20-2

0.55

28

Di-n-octyl phthalate

117-84-0

0.017

28

Di-n-propylnitrosamine

621-64-7

0.4

14

1,4-Dioxane

123-91-1

12

170

Diphenylamine (difficult to distinguish from diphenylnitrosamine)

122-39-4

0.92

NA

Diphenylnitrosamine (difficult to distinguish from diphenylamine)

86-30-6

0.92

NA

1,2-Diphenylhydrazine

122-66-7

0.087

NA

Disulfoton

298-04-4

0.017

6.2

Endosulfan I

939-98-8

0.023

0.066

Endosulfan II

33213-6-5

0.029

0.13

Endosulfan sulfate

1031-07-8

0.029

0.13

Endrin

72-20-8

0.0028

0.13

Endrin aldehyde

7421-93-4

0.025

0.13

Ethyl acetate

141-78-6

0.34

33

Ethyl cyanide (Propanenitrile)

107-12-0

0.24

360

Ethyl benzene

100-41-4

0.057

10

Ethyl ether

60-29-7

0.12

160

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

Ethyl methacrylate

97-63-2

0.14

160

Ethylene oxide

75-21-8

0.12

NA

Famphur

52-85-7

0.017

15

Fluoranthene

206-44-0

0.068

3.4

Fluorene

86-73-7

0.059

3.4

Heptachlor

76-44-8

0.0012

0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin, (1,2,3,4,6,7,8-HpCDD)

35822-46-9

0.000035

0.0025

1, 2,3,4,6,7,8-Heptachlorodibenzofuran, (1,2,3,4,6,7,8-HpCDF)

67562-39-4

0.000035

0.0025

1,2,3,4,7,8,9-Heptachlorodibenzofuran, (1,2,3,4,7,8,9-HpCDF)

55673-89-7

0.000035

0.0025

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

Hexachloroethane

67-72-1

0.055

30

Hexachloropropylene

1888-71-7

0.035

30

Indeno (1,2,3-c,d) pyrene

193-39-5

0.0055

3.4

Indomethane

74-88-4

0.019

65

Isobutyl alcohol

78-83-1

5.6

170

Isodrin

465-73-6

0.021

0.066

Isosafrole

120-58-1

0.081

2.6

Kepone

143-50-8

0.0011

0.13

Methacylonitrile

126-98-7

0.24

84

Methanol

67-56-1

5.6

NA

Methapyrilene

91-80-5

0.081

1.5

Methoxychlor

72-43-5

0.25

0.18

3-Methylcholanthrene

56-49-5

0.0055

15

4,4-Methylene bis(2-chloroaniline)

101-14-4

0.5

30

Methylene chloride

75-09-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Methyl isobutyl ketone

108-10-1

0.14

33

Methyl methacrylate

80-62-6

0.14

160

Methyl methanesulfonate

66-27-3

0.018

NA

Methyl parathion

298-00-0

0.014

4.6

Naphthalene

91-20-3

0.059

5.6

2-Naphthylamine

91-59-8

0.52

NA

p-Nitroaniline

100-01-6

0.028

28

Nitrobenzene

98-95-3

0.068

14

5-Nitro-o-toluidine

99-55-8

0.32

28

p-Nitrophenol

100-02-7

0.12

29

N-Nitrosodiethylamine

55-18-5

0.4

28

N-Nitrosodimethylamine

62-75-9

0.4

NA

N-Nitroso-di-n-butylamine

924-16-3

0.4

17

N-Nitrosomethylethylamine

10595-95-6

0.4

2.3

N-Nitrosomorpholine

59-89-2

0.4

2.3

N-Nitrosopiperidine

100-75-4

0.013

35

N-Nitrosopyrrolidine

930-55-2

0.013

35

1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin, (OCDD)

3268-87-9

0.000063

0.005

1,2,3,4,6,7,8,9-Octachlorodibenzofuran, (OCDF)

39001-02-0

0.000063

0.005

Parathion

56-38-2

0.014

4.6

Total PCBs (sum of all PCB isomers, or all Aroclors)

1336-36-3

0.1

10

Pentachlorobenzene

608-93-5

0.055

10

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

Pentachloronitrobenzene

82-68-8

0.055

4.8

Pentachlorophenol

87-86-5

0.089

7.4

Phenacetin

62-44-2

0.081

16

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Phorate

298-02-2

0.021

4.6

Phthalic anhydride

85-44-9

0.055

NA

Pronamide

23950-58-5

0.093

1.5

Pyrene

129-00-0

0.067

8.2

Pyridine

110-86-1

0.014

16

Safrole

94-59-7

0.081

22

Silvex (2,4,5-TP)

93-72-1

0.72

7.9

2,4,5-T

93-76-5

0.72

7.9

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

Toluene

108-88-3

0.08

10

Toxaphene

8001-35-2

0.0095

2.6

Bromoform (Tribromomethane)

75-25-2

0.63

15

1,2,4-Trichlorobenzene

120-82-1

0.055

19

1,1,1-Trichloroethane

71-55-6

0.054

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Trichlorofluoromethane

75-69-4

0.02

30

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

1,2,3-Trichloropropane

96-18-4

0.85

30

1,1,2-Trichloro-1,2,2-trifluoroethane

76-13-1

0.057

30

tris(2,3-Dibromopropyl) phosphate

126-72-7

0.11

NA

Vinyl chloride

75-01-4

0.27

6.0

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Barium

7440-39-3

1.2

21 mg/L TCLP

Beryllium

7440-41-7

0.82

NA

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

NA

Fluoride

16984-48-8

35

NA

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

0.15

0.25 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

Silver

7440-22-4

0.43

0.14 mg/L TCLP

Sulfide

8496-25-8

14

NA

Thallium

7440-28-0

1.4

NA

Vanadium

7440-62-2

4.3

NA

Hazardous Industrial Waste from Specific Sources

Hazardous Industrial Waste

Regulated Constituents
(and Treatment Subcategories1)

Land Disposal Treatment Requirements

Aqueous Waste

Non-aqueous Waste

Column 1

Column 2

Column 3

Column 4

Column 5

Column 6

Haz. Waste Number2

Waste

Generic Name or other description

CAS Number3

Treatment Code4 or Concentration5 (mg/L)

Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated)

Wood preservation:

K001

Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote and/or pentachlorophenol.

Naphthalene

91-20-3

0.059

5.6

Pentachlorophenol

87-86-5

0.089

7.4

Phenanthrene

85-01-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Inorganic Pigments:

K002

Wastewater treatment sludge from the production of chrome yellow and orange pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

 

 

 

 

K003

Wastewater treatment sludge from the production of molybdate orange pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

 

 

 

 

K004

Wastewater treatment sludge from the production of zinc yellow pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

K005

Wastewater treatment sludge from the production of chrome green pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

K006

Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated).

Treatment Subcategory 1

Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous):

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Treatment Subcategory 2

Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated):

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

K007

Wastewater treatment sludge from the production of iron blue pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

 

 

 

 

K008

Oven residue from the production of chrome oxide green pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Organic chemicals:

K009

Distillation bottoms from the production of acetaldehyde from ethylene.

Chloroform

67-66-3

0.046

6.0

K010

Distillation side cuts from the production of acetaldehyde from ethylene.

Chloroform

67-66-3

0.046

6.0

K011

Bottom stream from the wastewater stripper in the production of acrylonitrile.

Acetonitrile

75-05-8

5.6

38

Acrylonitrile

107-13-1

0.24

84

Acrylamide

79-06-1

19

23

Benzene

71-43-2

0.14

10

Cyanide (Total)7

57-12-5

1.2

590

K013

Bottom stream from the acetonitrile column in the production of acrylonitrile.

Acetonitrile

75-05-8

5.6

38

Acrylonitrile

107-13-1

0.24

84

Acrylamide

79-06-1

19

23

Benzene

71-43-2

0.14

10

Cyanide (Total)7

57-12-5

1.2

590

K014

Bottoms from the acetonitrile purification column in the production of acrylonitrile.

Acetonitrile

75-05-8

5.6

38

Acrylonitrile

107-13-1

0.24

84

Acrylamide

79-06-1

19

23

Benzene

71-43-2

0.14

10

Cyanide (Total)7

57-12-5

1.2

590

K015

Still bottoms from the distillation of benzyl chloride.

Anthracene

120-12-7

0.059

3.4

Benzal chloride

98-87-3

0.055

6.0

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Phenanthrene

85-01-8

0.059

5.6

Toluene

108-88-3

0.08

10

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

K016

Heavy ends or distillation residues from the production of carbon tetrachloride.

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

Hexachloroethane

67-72-1

0.055

30

Tetrachloroethylene

127-18-4

0.056

6.0

K017

Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

1,2-Dichloropropane

78-87-5

0.85

18

1,2,3-Trichloropropane

96-18-4

0.85

30

K018

Heavy ends from the fractionation column in ethyl chloride production.

Chloroethane

75-00-3

0.27

6.0

Chloromethane

74-87-3

0.19

NA

1,1-Dichloroethane

75-34-3

0.059

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Pentachloroethane

76-01-7

NA

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

K019

Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

Chlorobenzene

108-90-7

0.057

6.0

Chloroform

67-66-3

0.046

6.0

p-Dichlorobenzene

106-46-7

0.09

NA

1,2-Dichloroethane

107-06-2

0.21

6.0

Fluorene

86-73-7

0.059

NA

Hexachloroethane

67-72-1

0.055

30

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

NA

Tetrachloroethylene

127-18-4

0.056

6.0

1,2,4-Trichlorobenzene

120-82-1

0.055

19

1,1,1-Trichloroethane

71-55-6

0.054

6.0

K020

Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.

1,2-Dichloroethane

107-06-2

0.21

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

 

 

 

 

K021

Aqueous spent antimony catalyst waste from fluoromethanes production.

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

K022

Distillation bottom tars from the production of phenol/acetone from cumene.

Toluene

108-88-3

0.08

10

Acetophenone

96-86-2

0.01

9.7

Diphenylamine (difficult to distinguish from diphenylnitrosamine)

122-39-4

0.92

13

Diphenylnitrosamine (difficult to distinguish from diphenylamine)

86-30-6

0.92

13

Phenol

108-95-2

0.039

6.2

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

K023

Distillation light ends from the production of phthalic anhydride from naphthalene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0;
85-44-9

0.055

28

K024

Distillation bottoms from the production of phthalic anhydride from naphthalene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0;
85-44-9

0.055

28

K025

Distillation bottoms from the production of nitrobenzene by the nitration of benzene.

Distillation bottoms from the production of nitrobenzene by the nitration of benzene.

NA

LLEXT fb SSTRP fb CARBN; or CMBST

CMBST

K026

Stripping still tails from the production of methyl ethyl pyridines.

Stripping still tails from the production of methyl ethyl pyridines.

NA

CMBST

CMBST

K027

Centrifuge and distillation residues from toluene diisocyanate production.

Centrifuge and distillation residues from toluene diisocyanate production.

NA

CARBN; or CMBST

CMBST

K028

Spent catalyst from the hydrochlorinator reactor in the productions of 1,1,1trichloroethane.

1,1-Dichloroethane

75-34-3

0.059

6.0

trans-1,2-Dichloroethylene

156-60-5

0.054

30

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Pentachloroethane

76-01-7

NA

6.0

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Cadmium

7440-43-9

0.69

NA

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

K029

Waste from the product stream stripper in the production of 1,1,1trichloroethane.

Chloroform

67-66-3

0.046

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

1,1-Dichloroethylene

75-35-4

0.025

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

Vinyl chloride

75-01-4

0.27

6.0

K030

Column bottoms or heavy ends from the combined production of trichloroethylene and perchloroethylene.

o-Dichlorobenzene

95-50-1

0.088

NA

p-Dichlorobenzene

106-46-7

0.09

NA

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Hexachloropropylene

1888-71-7

NA

30

Pentachlorobenzene

608-93-5

NA

10

Pentachloroethane

76-01-7

NA

6.0

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

Tetrachloroethylene

127-18-4

0.056

6

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K083

Distillation bottoms from aniline production.

Aniline

62-53-3

0.81

14

Benzene

71-43-2

0.14

10

Cyclohexanone

108-94-1

0.36

NA

Diphenylamine (difficult to distinguish from diphenylnitrosamine

122-39-4

0.92

13

Diphenylnitrosamine (difficult to distinguish from diphenylamine)

86-30-6

0.92

13

Nitrobenzene

98-95-3

0.068

14

Phenol

108-95-2

0.039

6.2

Nickel

7440-02-0

3.98

11 mg/L TCLP

K085

Distillation or fractionation column bottoms from the production of chlorobenzenes.

Benzene

71-43-2

0.14

10

Chlorobenzene

108-90-7

0.057

6.0

m-Dichlorobenzene

541-73-1

0.036

6.0

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.09

6.0

Hexachlorobenzene

118-74-1

0.055

10

Total PCBs (sum of all PCB isomers, or all Aroclors)

1336-36-3

0.1

10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K093

Distillation light ends from the production of phthalic anhydride from orthoxylene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0;
85-44-9

0.055

28

K094

Distillation bottoms from the production of phthalic anhydride from orthoxylene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0;
85-44-9

0.055

28

K095

Distillation bottoms from the production of 1,1,1trichloroethane.

Hexachloroethane

67-72-1

0.055

30

Pentachloroethane

76-01-7

0.055

6.0

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-1

0.054

6.0

K096

Heavy ends from the heavy ends column from the production of 1,1,1trichloroethane.

m-Dichlorobenzene

541-73-1

0.036

6.0

Pentachloroethane

76-01-1

0.055

6.0

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,2,4-Trichlorobenzene

120-82-1

0.055

19

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

K103

Process residues from aniline extraction from the production of aniline.

Aniline

62-53-3

0.81

14

Benzene

71-43-2

0.14

10

2,4-Dinitrophenol

51-28-5

0.12

160

Nitrobenzene

98-95-3

0.068

14

Phenol

108-95-2

0.039

6.2

K104

Combined wastewater streams generated from nitrobenzene/aniline production.

Aniline

62-53-3

0.81

14

Benzene

71-43-2

0.14

10

2,4-Dinitrophenol

51-28-5

0.12

160

Nitrobenzene

98-95-3

0.068

14

Phenol

108-95-2

0.039

6.2

Cyanides (Total)7

57-12-5

1.2

590

K105

Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes.

Benzene

71-43-2

0.14

10

Chlorobenzene

108-90-7

0.057

6.0

2-Chlorophenol

95-57-8

0.044

5.7

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.09

6.0

Phenol

108-95-2

0.039

6.2

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

K107

Column bottoms from product separation from the production of 1,1-dimethyl-hydra-zine (UDMH) from carboxylic acid hydrazines.

Column bottoms from product separation from the production of 1,1-dimethyl-hydra-zine (UDMH) from carboxylic acid hydrazines.

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K108

Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K109

Spent filter cartridges from product purification from the production of 1,1- dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

Spent filter cartridges from product purification from the production of 1,1- dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K110

Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K111

Product washwaters from the production of dinitrotoluene via nitration of toluene.

2,4-Dinitrotoluene

121-1-2

0.32

140

2,6-Dinitrotoluene

606-20-2

0.55

28

K112

Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene.

Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K113

Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

CARBN; or CMBST

CMBST

K114

Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

CARBN; or CMBST

CMBST

K115

Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

Nickel

7440-02-0

3.98

11 mg/L TCLP

Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

CARBN; or CMBST

CMBST

K116

Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.

Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.

NA

CARBN; or CMBST

CMBST

K117

Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

Chloroform

67-66-3

0.046

6.0

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

K118

Spent adsorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

Chloroform

67-66-3

0.046

6.0

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

K136

Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

Chloroform

67-66-3

0.46

6.0

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

K149

Distillation bottoms from the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. (This waste does not include still bottoms from the distillation of benzyl chloride.)

Chlorobenzene

108-90-7

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Chloromethane

74-87-3

0.19

30

p-Dichlorobenzene

106-46-7

0.09

6.0

Hexachlorobenzene

118-74-1

0.055

10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

Toluene

108-88-3

0.08

10

K150

Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of alpha-( or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Chloromethane

74-87-3

0.019

30

p-Dichlorobenzene

106-46-7

0.09

6.0

Hexachlorobenzene

118-74-1

0.055

10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

1,1,2,2-Tetrachloroethane

79-34-5

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K151

Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.

Benzene

71-43-2

0.14

10

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Hexachlorobenzene

118-74-1

0.055

10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

Tetrachloroethylene

127-18-4

0.056

6.0

Toluene

108-88-3

0.08

10

 

 

 

 

K156

Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2- propynyl n-butylcarbamate.)

Acetonitrile

75-05-8

5.6

1.8

Acetophenone

96-86-2

0.01

9.7

Aniline

62-53-3

0.81

14

Benomyl

17804-35-2

0.056

1.4

Benzene

71-43-2

0.14

10

Carbaryl

63-25-2

0.006

0.14

Carbenzadim

10605-21-7

0.056

1.4

Carbofuran

1563-66-2

0.006

0.14

Carbosulfan

55285-14-8

0.028

1.4

Chlorobenzene

108-90-7

0.057

6.0

Chloroform

67-66-3

0.046

6.0

o-Dichlorobenzene

95-50-1

0.088

6.0

Methomyl

16752-77-5

0.028

0.14

Methylene chloride

75-09-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Naphthalene

91-20-3

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyridine

110-86-1

0.014

16

Toluene

108-88-3

0.08

10

Triethylamine

101-44-8

0.081

1.5

K157

Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Chloromethane

74-87-3

0.19

30

Methomyl

16752-77-5

0.028

0.14

Methylene chloride

75-09-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Pyridine

110-86-1

0.014

16

Triethylamine

121-44-8

0.081

1.5

 

 

 

 

K158

Bag house dusts and filter/separation solids from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)

Benomyl

17804-35-2

0.056

1.4

Benzene

71-43-2

0.14

10

Carbenzadim

10605-21-7

0.056

1.4

Carbofuran

1563-66-2

0.006

0.14

Carbosulfan

55285-14-8

0.028

1.4

Chloroform

67-66-3

0.046

6.0

Methylene chloride

75-09-2

0.089

30

Phenol

108-95-2

0.039

6.2

K159

Organics from the treatment of thiocarbamate wastes.

Benzene

71-43-2

0.14

10

Butylate

2008-41-5

0.042

1.4

EPTC (Eptam)

759-94-4

0.042

1.4

Molinate

2212-67-1

0.042

1.4

Pebulate

1114-71-2

0.042

1.4

Vernolate

1929-77-7

0.042

1.4

K161

Purification solids (including filtration, evaporation, and centrifugation solids), bag house dust and floor sweepings from the production of dithiocarbamate acids and their salts. (This listing does not include K125 or K126.)

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Carbon disulfide

75-15-0

3.8

4.8 mg/L TCLP

Dithiocarbamates (total)

NA

0.028

28

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11.0 mg/L TCLP

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

K174

Wastewater treatment sludges from the production of ethylene dichloride or vinyl chloride monomer.

1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD)

35822-46-9

0.000035 or CMBST8

0.0025 or CMBST8

1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF)

67562-39-4

0.000035 or CMBST8

0.0025 or CMBST8

1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF)

55673-89-7

0.000035 or CMBST8

0.0025 or CMBST8

HxCDDs (All Hexachlorodibenzo-p-dioxins)

34465-46-8

0.000063 or CMBST8

0.001 or CMBST8

HxCDFs (All Hexachlorodibenzofurans)

55684-94-1

0.000063 or CMBST8

0.001 or CMBST8

1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (OCDD)

3268-87-9

0.000063 or CMBST8

0.005 or CMBST8

1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF)

39001-02-0

0.000063 or CMBST8

 0.005 or CMBST8

PeCDDs (All Pentachlorodibenzo-p-dioxins

36088-22-9

0.000063 or CMBST8

0.001 or CMBST8

PeCDFs (All Pentachlorodibenzofurans)

30402-15-4

0.000035 or CMBST8

0.001 or CMBST8

TCDDs (All tetachlorodibenzo-p-dioxins)

41903-57-5

0.000063 or CMBST8

0.001 or CMBST8

TCDFs (All tetrachlorodibenzofurans)

55722-27-5

0.000063 or CMBST8

0.001 or CMBST8

Arsenic

7440-36-0

1.4

5.0 mg/L TCLP

K175

Wastewater treatment sludge from the production of vinyl chloride monomer using mercuric chloride catalyst in an acetylene-based process.

Mercury

7438-97-6

0.15

0.025 mg/L TCLP10

pH

 

NA

pH≤ 6.010

Inorganic chemicals:

K071

Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used.

Treatment Subcategory 1

Non-aqueous wastes that are residues from RMERC:

Mercury

7439-97-6

NA

0.20 mg/L TCLP

Treatment Subcategory 2

Non-aqueous wastes that are not residues from RMERC:

Mercury

7439-97-6

NA

0.025 mg/L TCLP

Treatment Subcategory 3

All K071 aqueous wastes:

Mercury

7439-97-6

0.15

NA

K073

Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production.

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Hexachloroethane

67-72-1

0.055

30

Tetrachloroethylene

127-18-4

0.056

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

K106

Wastewater treatment sludge from the mercury cell process in chlorine production.

Treatment Subcategory 1

Non-aqueous wastes that contain greater than or equal to 260 mg/kg total mercury:

Mercury

7439-97-6

NA

RMERC

Treatment Subcategory 2

Non-aqueous wastes that contain less than 260 mg/kg total mercury that are residues from RMERC:

Mercury

7439-97-6

NA

0.20 mg/L TCLP

Treatment Subcategory 3

Other K106 non-aqueous wastes that contain less than 260 mg/kg total mercury and are not residues from RMERC:

Mercury

7439-97-6

NA

0.025 mg/L TCLP

Treatment Subcategory 4

All K106 aqueous wastes:

Mercury

7439-97-6

0.15

NA

K176

Baghouse filters from the production of antimony oxide, including filters from the production of intermediates (e.g., antimony metal or crude antimony oxide).

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

0.15

0.025 mg/L TCLP

 

 

 

 

K177

Slag from the production of antimony oxide that is speculatively accumulated or disposed, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide).

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

 

 

 

 

K178

Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process.

1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD)

35822-46-9

0.000035 or CMBST8

0.0025 or CMBST8

1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF)

67562-39-4

0.000035 or CMBST8

0.0025 or CMBST8

1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF)

55673-89-7

0.000035 or CMBST8

0.0025 or CMBST8

HxCDDs (All Hexachlorodibenzo-p-dioxins)

34465-46-8

0.000063 or CMBST8

0.001 or CMBST8

HxCDFs (All Hexachlorodibenzofurans)

55684-94-1

0.000063 or CMBST8

0.001 or CMBST8

1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (OCDD)

3268-87-9

0.000063 or CMBST8

0.005 or CMBST8

1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF)

39001-02-0

0.000063 or CMBST8

0.005 or CMBST8

PeCDDs (All Pentachlorodibenzo-p-dioxins

36088-22-9

0.000063 or CMBST8

0.001 or CMBST8

PeCDFs (All Pentachlorodibenzofurans)

30402-15-4

0.000035 or CMBST8

0.001 or CMBST8

TCDDs (All tetachlorodibenzo-p-dioxins)

41903-57-5

0.000063 or CMBST8

0.001 or CMBST8

TCDFs (All tetrachlorodibenzofurans)

55722-27-5

0.000063 or CMBST8

0.001 or CMBST8

Thallium

7440-28-0

1.4

0.20 mg/L TCLP

Pesticides:

K031

Byproduct salts generated in the production of MSMA and cacodylic acid.

Arsenic

7440-38-2

14

5.0 mg/L TCLP

K032

Wastewater treatment sludge from the production of chlordane.

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

Heptachlor

76-44-8

0.0012

0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

K033

Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane.

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

K034

Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

K035

Wastewater treatment sludges generated in the production of creosote.

Acenaphthene

83-32-9

NA

3.4

Anthracene

120-12-7

NA

3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Bemzo(a)pyrene

50-32-8

0.061

3.4

Chrysene

218-01-9

0.059

3.4

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p- cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m- cresol)

106-44-5

0.77

5.6

Dibenz(a,h)anthracene

53-70-3

NA

8.2

Fluoranthene

206-44-0

0.068

3.4

Fluorene

86-73-7

NA

3.4

Indeno(1,2,3-cd)pyrene

193-39-5

NA

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-1

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

K036

Still bottoms from toluene reclamation distillation in the production of disulphoton.

Disulfoton

298-04-4

0.017

6.2

K037

Wastewater treatment sludges from the production of disulphoton.

Disulfoton

298-04-4

0.017

6.2

Toluene

108-88-3

0.08

10

K038

Wastewater from the washing and stripping of phorate production.

Phorate

298-02-2

0.021

4.6

K039

Filter cake from the filtration of diethyl phosphorodithioic acid in the production of phorate.

Filter cake from the filtration of diethyl phosphorodithioic acid in the production of phorate.

NA

CARBN; or CMBST

CMBST

K040

Wastewater treatment sludge from the production of phorate.

Phorate

298-02-2

0.021

4.6

K041

Wastewater treatment sludge from the production of toxaphene.

Toxaphene

8001-35-2

0.0095

2.6

K042

Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5T.

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.09

6.0

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K043

2,6-Dichlorophenol waste from the production of 2,4D.

2,4-Dichlorophenol

120-83-2

0.044

14

2,6-Dichlorophenol

187-65-0

0.044

14

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

Pentachlorophenol

87-86-5

0.089

7.4

Tetrachloroethylene

127-18-4

0.056

6.0

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

K097

Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

Heptachlor

76-44-8

0.0012

0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

K098

Untreated process wastewater from the production of toxaphene.

Toxaphene

8001-35-2

0.0095

2.6

K099

Untreated wastewater from the production of 2,4-D.

2,4-Dichlorophenoxyacetic acid

94-75-7

0.72

10

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

K123

Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salt.

Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salt.

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K124

Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.

Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K125

Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.

Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K126

Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.

Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K131

Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

K132

Spent absorbent and wastewater separator solids from the production of methyl bromide.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

Explosives:

K044

Wastewater treatment sludges from the manufacturing and processing of explosives.

Wastewater treatment sludges from the manufacturing and processing of explosives.

NA

DEACT

DEACT

K045

Spent carbon from the treatment of wastewater containing explosives.

Spent carbon from the treatment of wastewater containing explosives.

NA

DEACT

DEACT

K046

Wastewater treatment sludges from the manufacturing formulation and loading of leadbased initiating compounds.

Lead

7439-92-1

0.69

0.75 mg/L TCLP

K047

Pink/red water from TNT operations.

Pink/red water from TNT operations.

NA

DEACT

DEACT

Petroleum refining:

K048

Dissolved air flotation (DAF) float from the petroleum refining industry.

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Chrysene

218-01-9

0.059

3.4

Di-n-butyl phthalate

84-74-2

0.057

28

Ethylbenzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

NA

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-33

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K049

Slop oil emulsion solids from the petroleum refining industry.

Anthracene

120-12-7

0.059

3.4

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Carbon disulfide

75-15-0

3.8

NA

Chrysene

2218/01/09

0.059

3.4

2,4-Dimethylphenol

105-67-9

0.036

NA

Ethylbenzene

100-41-4

0.057

10

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Cyanides (Total)7

57-12-5

1.2

590

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K050

Heat exchanger bundle cleaning sludge from the petroleum refining industry.

Benzo(a)pyrene

50-32-8

0.061

3.4

Phenol

108-95-2

0.039

6.2

Cyanides (Total)7

57-12-5

1.2

590

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K051

API separator sludge from the petroleum refining industry.

Acenaphthene

83-32-9

0.059

NA

Anthracene

120-12-7

0.059

3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Chrysene

2218/01/09

0.059

3.4

Di-n-butyl phthalate

105-67-9

0.057

28

Ethylbenzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

NA

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Cyanides (Total)7

57-12-5

1.2

590

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K052

Tank bottoms (leaded) from the petroleum refining industry.

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p-cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m-cresol

106-44-5

0.77

5.6

2,4-Dimethylphenol

105-67-9

0.036

NA

Ethylbenzene

100-41-4

0.057

10

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K169

Crude oil storage tank sediment from petroleum refining operations.

Benz(a)anthracene

56-55-3

0.059

3.4

Benzene

71-43-2

0.14

10

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Chrysene

218-01-9

0.059

3.4

Ethyl benzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

81-05-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Toluene (Methyl Benzene)

108-88-3

0.08

10

Xylene(s) (Total)

1330-20-7

0.32

30

K170

Clarified slurry oil tank sediment and/or in-line filter/separation solids from petroleum refining operations.

Benz(a)anthracene

56-55-3

0.059

3.4

Benzene

71-43-2

0.14

10

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Ethyl benzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

3.4

Indeno(1,3,4-cd)pyrene

193-39-5

0.0055

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

81-05-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Toluene (Methyl Benzene)

108-88-3

0.08

10

Xylene(s) (Total)

1330-20-7

0.32

30

K171

Spent Hydrotreating catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media).

Benz(a)anthracene

56-55-3

0.059

3.4

Benzene

71-43-2

0.14

10

Chrysene

218-01-9

0.059

3.4

Ethyl benzene

100-41-4

0.057

10

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

81-05-8

0.059

5.6

Pyrene

129-00-0

0.67

8.2

Toluene (Methyl Benzene)

108-88-3

0.08

10

Xylene(s) (Total)

1330-20-7

0.32

30

Arsenic

7740-38-2

1.4

5 mg/L TCLP

Nickel

7440-02-0

3.98

11.0 mg/L TCLP

Vanadium

7440-62-2

4.3

1.6 mg/L TCLP

Reactive sulfides

NA

DEACT

DEACT

K172

Spent Hydrorefining catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media).

Benzene

71-43-2

0.14

10

Ethyl benzene

100-41-4

0.57

10

Toluene (Methyl Benzene)

108-88-3

0.08

10

Xylene(s) (Total)

1330-20-7

0.32

30

Antimony

7740-36-0

1.9

1.15 mg/L TCLP

Arsenic

7740-38-2

1.4

5 mg/L TCLP

Nickel

7440-02-0

3.98

11.0 mg/L TCLP

Vanadium

7440-62-2

4.3

1.6 mg/L TCLP

Reactive sulfides

NA

DEACT

DEACT

Iron and steel:

K061

Emission control dust/sludge from the primary production of steel in electric furnaces.

Antimony

7440-36-0

NA

1.15 mg/L TCLP

Arsenic

7440-38-2

NA

5.0 mg/L TCLP

Barium

7440-39-3

NA

21 mg/L TCLP

Beryllium

7440-41-7

NA

1.22 mg/L TCLP

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

NA

0.025 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Selenium

7782-49-2

NA

5.7 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

Thallium

7440-28-0

NA

0.20 mg/L TCLP

Zinc

7440-66-6

NA

4.3 mg/L TCLP

K062

Spent pickle liquor generated by steel finishing operations within the iron and steel industry at steel works, blast furnaces (including coke ovens), rolling mills, iron and steel foundries, gray and ductile iron foundries, malleable iron foundries, steel investment foundries or other miscellaneous steel foundries or at facilities in the electrometallurgical products (except steel) industry, steel wiredrawing and steel nails and spikes industry, cold-rolled steel sheet, strip and bars industry, or steel pipe and tubes industry.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

NA

 

 

 

 

Primary aluminum:

K088

Spent potliners from primary aluminum reduction.

Acenaphthene

83-32-9

0.059

3.4

Anthracene

120-12-7

0.059

3.4

Bemz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene

205-99-2

0.11

6.8

Benzo(k)fluoranthene

207-08-9

0.11

6.8

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Fluoranthene

206-44-0

0.068

3.4

Indeno(1,2,3,-c,d)pyrene

193-39-5

0.0055

3.4

Phenanthrene

85-01-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

26.1

Barium

7440-39-3

1.2

21 mg/L TCLP

Beryllium

7440-41-7

0.82

1.22 mg/L TCLP

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

0.15

0.025 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

Silver

7440-22-4

0.43

0.14 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Fluoride

16984-48-8

35

NA

Secondary lead:

K069

Emission control dust/sludge from secondary lead smelting, not including sludge generated from secondary acid scrubber systems.

Treatment Subcategory 1

Calcium Sulfate (Low Lead)

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Treatment Subcategory 2

Non- Calcium Sulfate (High Lead)

Non- Calcium Sulfate (High Lead)

NA

NA

RLEAD

K100

Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting.

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Veterinary pharmaceuticals:

K084

Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

K101

Distillation tar residues from the distillation of anilinebased compounds in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.

o-Nitroaniline

88-74-4

0.27

14

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Cadmium

7440-43-9

0.69

NA

Lead

7439-92-1

0.69

NA

Mercury

7439-97-6

0.15

NA

K102

Residue from the use of activated carbon for decolourization in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.

o-Nitrophenol

88-75-5

0.028

13

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Cadmium

7440-43-9

0.69

NA

Lead

7439-92-1

0.69

NA

Mercury

7439-97-6

0.15

NA

Ink formulation:

K086

Solvent washes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, driers, soaps, and stabilizers containing chromium and lead.

Acetone

67-64-1

0.28

160

Acetophenone

96-86-2

0.01

9.7

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

n-Butyl alcohol

71-36-3

5.6

2.6

Butylbenzyl phthalate

85-68-7

0.017

28

Cyclohexanone

108-94-1

0.36

NA

o-Dichlorobenzene

95-50-1

0.088

6.0

Diethyl phthalate

84-66-2

0.2

28

Dimethyl phthalate

131-11-3

0.047

28

Di-n-butyl phthalate

84-74-2

0.057

28

Di-n-octyl phthalate

117-84-0

0.017

28

Ethyl acetate

141-78-6

0.34

33

Ethylbenzene

100-41-4

0.057

10

Methanol

67-56-1

5.6

NA

Methyl ethyl ketone

78-93-3

0.28

36

Methyl isobutyl ketone

108-10-1

0.14

33

Methylene chloride

75-09-2

0.089

30

Naphthalene

91-20-3

0.059

5.6

Nitrobenzene

98-95-3

0.068

14

Toluene

108-88-3

0.08

10

1,1,1-Trichloroethane

71-55-6

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Coking:

K060

Ammonia still lime sludge from coking operations.

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

Naphthalene

91-20-3

0.059

5.6

Phenol

108-95-2

0.039

6.2

Cyanides (Total)7

57-12-5

1.2

590

K087

Decanter tank tar sludge from coking operations.

Acenaphthylene

208-96-8

0.059

3.4

Benzene

71-43-2

0.14

10

Chrysene

218-01-9

0.059

3.4

Fluoranthene

206-44-0

0.068

3.4

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

K141

Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke from coal or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludges from coking operations).

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-2-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

K142

Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

K143

Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal.

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

K144

Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal.

Benzene

71-43-2

0.14

10

Benz(a)pyrene

56-55-3

0.059

3.4

Benzo(a)anthracene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

K145

Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Naphthalene

91-20-3

0.059

5.6

K147

Tar storage tank residues from coal tar refining.

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

K148

Residues from coal tar distillation, including but not limited to, still bottoms.

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

Notes to Schedule 1:

1 Treatment subcategories are shown for some wastes.  In these cases, it is necessary to identify the treatment subcategory that most closely describes the particular waste for which treatment is required.  The land disposal treatment requirements for that waste are those shown for that treatment subcategory.

2 Haz. Waste Number means Hazardous Waste Number.  These numbers are consistent with United States Environmental Protection Agency Hazardous Waste Numbers.  If there is no United States Environmental Protection Agency Hazardous Waste Number for a waste, the Hazardous Waste Number is assigned to the waste by the Ontario Ministry of the Environment.

3 CAS Number means the Chemical Abstracts Service Registry Number.  When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only.

4 See Schedule 7 for a description of the treatment methods and treatment standards associated with each treatment code.  In some cases, the entries in this Schedule may set out more than one treatment code for a regulated constituent.  An entry may permit a choice of treatment methods.  For example, the entry “CHOXD; BIODG; or CMBST” means that the waste may be treated using any of the treatment methods that are set out for those treatment codes in Schedule 7.  An entry may require treatment methods to be applied in a particular sequence.  For this purpose, the abbreviation “fb” means “followed by”.  For example, the entry “CHOXD fb CARBN” means that the waste must first be treated using the treatment method that is set out for CHOXD in Schedule 7 and, following that treatment, it must be treated using the treatment method that is set out for CARBN in Schedule 7.  An entry may combine a choice of treatment methods and a requirement to apply treatment methods in a particular sequence (for example, “(WETOX or CHOXD) fb CARBN; or CMBST”).

5 Concentration requirements for aqueous wastes are based on analysis of composite samples.

6 Concentration requirements for non-aqueous wastes are based on analysis of grab samples.

7 Both Cyanides (Total) and Cyanides (Amenable) for non-aqueous wastes are to be analyzed using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste, Physical/ Chemical Methods”, United States Environmental Protection Agency Publication SW–846, with a sample size of 10 grams and a distillation time of one hour and 15 minutes.

8 For these wastes, the treatment method described by the CMBST treatment code must be carried out at a facility that is authorized through a Certificate of Approval to treat these types of waste.

9 Resource Conservation and Recovery Act (RCRA), United States Congress, 42 U.S.C. s/s 6901 et seq. (1976), Subtitle C, Code of Federal Regulations, 40CFR, Chapter I - Environmental Protection Agency, Subchapter I - Solid Wastes, Part 261 - Identification and Listing of Hazardous Waste.

10 K175 non-aqueous wastes that have been treated in compliance with Schedule 1 land disposal treatment requirements must also be macroencapsulated in accordance with Schedule 8 (Alternative Treatment for Hazardous Debris), unless the waste is placed in:

(1) A hazardous waste monofill containing only K175 wastes that meet all applicable Schedule 1 treatment standards; or

(2) A dedicated hazardous waste landfill cell in which all other wastes being co-disposed are at pH≤ 6.0.

O. Reg. 461/05, s. 22.

See:  O. Reg. 461/05, ss. 22, 29 (3).

Schedule 1.1
EXEMPT HAZARDOUS INDUSTRIAL WASTES

Industry and Site

Waste

ICI Canada Inc., Cornwall

Brine purification muds (known either as K071 or No. NA9390, saturator and clarifier sludges only, without mixing with other wastes or materials) generated from mercury cells at the chloralkali chlorine plant.

Iron and steel industry, any site

Sludge generated by lime stabilization of spent pickle liquor (known either as K062 or No. NA9381) generated by steel finishing operations within the iron and steel industry at steel works, blast furnaces (including coke ovens), rolling mills, iron and steel foundries, gray and ductile iron foundries, malleable iron foundries, steel investment foundries or other miscellaneous steel foundries or at facilities in the electrometallurgical products (except steel) industry, steel wiredrawing and steel nails and spikes industry, cold-rolled steel sheet, strip and bars industry, or steel pipe and tubes industry.

Iron and steel industry, any site

Nonwastewater residues, such as slag, resulting from high temperature metals recovery (HTMR) processing of K061 (known also as No. NA9380) or K062 (known also as No. NA9381) waste, in units identified as rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations or industrial furnaces.

Electroplating industry, any site

Nonwastewater residues, such as slag, resulting from high temperature metals recovery (HTMR) processing of F006 (known also as No. NA9306) waste, in units identified as rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations or industrial furnaces.

Organic chemical industry, any site

Biological treatment sludge from the treatment of organic waste (K156) and wastewaters (K157) from the production of carbamates and carbamoyl oximes.

Petroleum refining industry, any site

Catalyst inert support media separated from spent hydrotreating catalyst (K171) or spent hydrorefining catalyst (K172).

O. Reg. 558/00, s. 4.

Note:  On January 1, 2007, Schedule 1.1 is revoked and the following substituted:

SCHEDULE 1.1
EXEMPT HAZARDOUS INDUSTRIAL WASTES

Industry and Site

Waste

ICI Canada Inc., Cornwall

Brine purification muds (K071), saturator and clarifier sludges only, without mixing with other wastes or materials) generated from mercury cells at the chloralkali chlorine plant.

Iron and steel industry, any site

Sludge generated by lime stabilization of spent pickle liquor (K062) generated by steel finishing operations within the iron and steel industry at steel works, blast furnaces (including coke ovens), rolling mills, iron and steel foundries, gray and ductile iron foundries, malleable iron foundries, steel investment foundries or other miscellaneous steel foundries or at facilities in the electrometallurgical products (except steel) industry, steel wiredrawing and steel nails and spikes industry, cold-rolled steel sheet, strip and bars industry, or steel pipe and tubes industry.

Iron and steel industry, any site

Nonwastewater residues, such as slag, resulting from high temperature metals recovery (HTMR) processing of K061 or K062 waste, in units identified as rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations or industrial furnaces.

Electroplating industry, any site

Nonwastewater residues, such as slag, resulting from high temperature metals recovery (HTMR) processing of F006 waste, in units identified as rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations or industrial furnaces.

Organic chemical industry, any site

Biological treatment sludge from the treatment of organic waste (K156) and wastewaters (K157) from the production of carbamates and carbamoyl oximes.

Petroleum refining industry, any site

Catalyst inert support media separated from spent hydrotreating catalyst (K171) or spent hydrorefining catalyst (K172).

O. Reg. 461/05, s. 23.

See:  O. Reg. 461/05, ss. 23, 29 (3).

 

Schedule 2
Part A — acute Hazardous Waste Chemicals

Hazardous Waste No.

Chemical Abstracts No.

Substance

Reference Number

P026

5344-82-1

1-(o-Chlorophenyl)thiourea

ON1037

P081

55-63-0

1,2,3-Propanetriol, trinitrate

ON1089

P042

51-43-4

1,2-Benzenediol,4-[1-hydroxy-2-(methylamino)ethyl]-

ON1025

P067

75-55-8

1,2-Propylenimine

ON1082

P185

26419-73-8

1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O-[(methylamino)-carbonyl]oxime

 

P004

309-00-2

1,4,5,8-Dimethanonaphthalene,1,2,3,4,10,10-hexa-chloro-1,4,4a,5,8,8a,-hexahydro-, (1alpha,4alpha, 4abeta, 5alpha,8alpha,8abeta)

ON1010

P060

465-73-6

1,4,5,8-Dimethanonaphthalene,1,2,3,4,10,10-hexa-chloro-1,4,4a,5,8,8a-hexahydro-,

(1alpha,4alpha, 4abeta, 5beta, 8beta, 8abeta)-

ON1070

P002

591-08-2

1-Acetyl-2-thiourea

ON1002

P048

51-28-5

2,4-Dinitrophenol

ON1055

P051

**72-20-8

2,7:3,6-Dimethanonaphth [2,3-b]oxirene, 3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-, (1aalpha,2beta,2abeta,3alpha,6alpha,6 abeta,7beta, 7aalpha)-, & metabolites

ON1062

P037

60-57-1

2,7:3,6-Dimethanonaphth[2,3-b]oxirene,3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-, (1aalpha,2beta,2aalpha,3beta,6beta,6a alpha,7beta, 7aalpha)-[b]oxirene, 3,4,5,6,9,9-hexachloro-

ON1043

P045

39196-18-4

2-Butanone,3,3-dimethyl-1-methylthio)-,O-[methylamino)carbonyl] oxime

ON1049

P034

131-89-5

2-Cyclohexyl-4,6-dinitrophenol

ON1054

P001

**81-81-2

2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, & salts, when present at concentrations greater than 0.3%

ON1006

P069

75-86-5

2-Methyllactonitrile

ON1005

P017

598-31-2

2-Propanone, 1-bromo-

ON1029

P005

107-18-6

2-Propen-1-ol

ON1011

P003

107-02-8

2-Propenal

ON1007

P102

107-19-7

2-Propyn-1-ol

ON1097

P007

2763-96-4

3(2H)-Isoxazolone, 5-(aminomethyl)-

ON1008

P027

542-76-7

3-Chloropropionitrile

ON1038

P202

64-00-6

3-Isopropylphenyl N-methylcarbamate

 

P047

**534-52-1

4,6-Dinitro-o-cresol, & salts

ON1053

P059

76-44-8

4,7-Methano-1H-indene, 1,4,5,6,7,8,8- heptachloro-3a,4,7,7a-tetrahydro-

ON1069

P008

504-24-5

4-Aminopyridine

ON1013

P008

504-24-5

4-Pyridinamine

ON1013

P007

2763-96-4

5-(Aminomethyl)-3-isoxazolol

ON1008

P050

115-29-7

6,9-Methano-2,4,3-benzodioxathiepin, 6,7,8,9, 10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide

ON1060

P127

1563-66-2

7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate

 

P088

145-73-3

7-Oxabicyclo[2.2.1]heptane-2,3-dicarboxylic acid

ON1061

P023

107-20-0

Acetaldehyde, chloro-

ON1001

P057

640-19-7

Acetamide, 2-fluoro-

ON1003

P002

591-08-2

Acetamide, N-(aminothioxomethyl)-

ON1002

P058

62-74-8

Acetic acid, fluoro-, sodium salt

ON1067

P003

107-02-8

Acrolein

ON1007

P070

116-06-3

Aldicarb

ON1009

P203

1646-88-4

Aldicarb sulfone

 

P004

309-00-2

Aldrin

ON1010

P005

107-18-6

Allyl alcohol

ON1011

P046

122-09-8

alpha,alpha-Dimethylphenethylamine

ON1052

P072

86-88-4

alpha-Naphthylthiourea

ON1083

P006

20859-73-8

Aluminum phosphide

ON1012

P009

131-74-8

Ammonium picrate

ON1015

P119

7803-55-6

Ammonium vanadate

ON1014

P099

506-61-6

Argentate(1-), bis(cyano-C)-, potassium

ON1096

P010

7778-39-4

Arsenic acid H3AsO4

ON1016

P012

1327-53-3

Arsenic oxide As2O3

ON1017

P011

1303-28-2

Arsenic oxide As2O5

ON1018

P011

1303-28-2

Arsenic pentoxide

ON1018

P012

1327-53-3

Arsenic trioxide

ON1017

P038

692-42-2

Arsine, diethyl-

ON1019

P036

696-28-6

Arsonous dichloride, phenyl-

ON1042

P054

151-56-4

Aziridine

ON1020

P067

75-55-8

Aziridine, 2-methyl-

ON1082

P013

542-62-1

Barium cyanide

ON1021

P024

106-47-8

Benzenamine, 4-chloro-

ON1022

P077

100-01-6

Benzenamine, 4-nitro-

ON1023

P028

100-44-7

Benzene, (chloromethyl)-

ON1024

P046

122-09-8

Benzeneethanamine, alpha,alpha-dimethyl-

ON1052

P014

108-98-5

Benzenethiol

ON1026

P188

57-64-7

Benzoic acid, 2-hydroxy-, compd. With (3aS-cis)-1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo[2,3-b]indol-5-yl methylcarbamate ester (1:1)

 

P028

100-44-7

Benzyl chloride

ON1024

P015

7440-41-7

Beryllium powder

ON1027

P017

598-31-2

Bromoacetone

ON1029

P018

357-57-3

Brucine

ON1030

P021

592-01-8

Calcium cyanide

ON1031

P021

592-01-8

Calcium cyanide Ca(CN)2

ON1031

P189

55285-14-8

Carbamic acid, [(dibutylamino)-thio]methyl-, 2,3-dihydro-2,2-dimethyl- 7-benzofuranyl ester

 

P191

644-64-4

Carbamic acid, dimethyl-, 1-[(dimethyl-amino)carbonyl]- 5-methyl-1H- pyrazol-3-yl este

 

P190

1129-41-5

Carbamic acid, methyl-, 3-methylphenyl ester

 

P192

119-38-0

Carbamic acid,dimethyl-,3-methyl-1-(1methylethyl)-1H-pyrazol-5-yl ester

 

P127

1563-66-2

Carbofuran

 

P022

75-15-0

Carbon disulfide

ON1034

P095

75-44-5

Carbonic dichloride

ON1035

P189

55285-14-8

Carbosulfan

 

P023

107-20-0

Chloroacetaldehyde

ON1001

P029

544-92-3

Copper cyanide

ON1039

P029

544-92-3

Copper cyanide Cu(CN)

ON1039

P030

N/A

Cyanides (soluble cyanide salts), not otherwise specified

ON1040

P031

460-19-5

Cyanogen

ON1041

P033

506-77-4

Cyanogen chloride

ON1036

P033

506-77-4

Cyanogen chloride (CN)Cl

ON1036

P016

542-88-1

Dichloromethyl ether

ON1028

P036

696-28-6

Dichlorophenylarsine

ON1042

P037

60-57-1

Dieldrin

ON1043

P038

692-42-2

Diethylarsine

ON1019

P041

311-45-5

Diethyl-p-nitrophenyl phosphate

ON1045

P043

55-91-4

Diisopropylfluorophosphate (DFP)

ON1047

P044

60-51-5

Dimethoate

ON1048

P191

644-64-4

Dimetilan.

 

P020

88-85-7

Dinoseb

ON1056

P085

152-16-9

Diphosphoramide, octamethyl-

ON1057

P111

107-49-3

Diphosphoric acid, tetraethyl ester

ON1098

P039

298-04-4

Disulfoton

ON1044

P049

541-53-7

Dithiobiuret

ON1058

P050

115-29-7

Endosulfan

ON1060

P088

145-73-3

Endothall

ON1061

P051

72-20-8

Endrin

ON1062

P051

72-20-8

Endrin, & metabolites

ON1062

P042

51-43-4

Epinephrine

ON1025

P031

460-19-5

Ethanedinitrile

ON1041

P194

23135-22-0

Ethanimidothioc acid, 2-(dimethylamino)-N-[[(methylamino)carbonyl]oxy]-2-oxo-, methyl ester

 

P066

16752-77-5

Ethanimidothioic acid, N-[[(methylamino)carbonyl]oxy]-,methyl ester

ON1004

P101

107-12-0

Ethyl cyanide

ON1064

P054

151-56-4

Ethyleneimine

ON1020

P097

52-85-7

Famphur

ON1065

P056

7782-41-4

Fluorine

ON1066

P057

640-19-7

Fluoroacetamide

ON1003

P058

62-74-8

Fluoroacetic acid, sodium salt

ON1067

P198

23422-53-9

Formetanate hydrochloride

 

P197

17702-57-7

Formparanate

 

P065

628-86-4

Fulminic acid, mercury(2+) salt

ON1068

P059

76-44-8

Heptachlor

ON1069

P062

757-58-4

Hexaethyl tetraphosphate

ON1072

P068

60-34-4

Hydrazine, methyl-

ON1074

P116

79-19-6

Hydrazinecarbothioamide

ON1073

P063

74-90-8

Hydrocyanic acid

ON1075

P063

74-90-8

Hydrogen cyanide

ON1075

P096

7803-51-2

Hydrogen phosphide

ON1077

P060

465-73-6

Isodrin

ON1070

P192

119-38-0

Isolan

 

P196

15339-36-3

Manganese dimethyl dithiocarbamate

 

P196

15339-36-3

Manganese,bis(dimethylcarbamodithioato-S,S')-

 

P202

64-00-6

M-Cumenyl methylcarbamate

 

P065

628-86-4

Mercury fulminate

ON1068

P092

62-38-4

Mercury, (acetato-O)phenyl-

ON1079

P082

62-75-9

Methanamine, N-methyl-N-nitroso-

ON1051

P064

624-83-9

Methane, isocyanato-

ON1078

P016

542-88-1

Methane, oxybis[chloro-

ON1028

P112

509-14-8

Methane, tetranitro-

ON1080

P118

75-70-7

Methanethiol, trichloro-

ON1081

P197

17702-57-7

Methanimidamide,N,N-dimethyl-N'-[2-methyl-4-[[(methylamino)carbonyl]oxy]phenyl]-

 

P198

23422-53-9

Methanimidamide,N,N-dimethyl-N'-[3-[[(methylamino)-carbonyl]oxy]phenyl]-, monohydrochloride

 

P199

2032-65-7

Methiocarb

 

P066

16752-77-5

Methomyl

ON1004

P068

60-34-4

Methyl hydrazine

ON1074

P064

624-83-9

Methyl isocyanate

ON1078

P071

298-00-0

Methyl parathion

ON1050

P190

1129-41-5

Metolcarb

 

P128

315-8-4

Mexacarbate

 

P073

13463-39-3

Nickel carbonyl

ON1084

P073

13463-39-3

Nickel carbonyl Ni(CO)4,(T-4)-

ON1084

P074

557-19-7

Nickel cyanide

ON1085

P074

557-19-7

Nickel cyanide Ni(CN)2

ON1085

P075

**54-11-5

Nicotine, & salts

ON1086

P076

10102-43-9

Nitric oxide

ON1087

P078

10102-44-0

Nitrogen dioxide

ON1088

P076

10102-43-9

Nitrogen oxide NO

ON1087

P078

10102-44-0

Nitrogen oxide NO2

ON1088

P081

55-63-0

Nitroglycerine

ON1089

P082

62-75-9

N-Nitrosodimethylamine

ON1051

P084

4549-40-0

N-Nitrosomethylvinylamine

ON1063

P040

297-97-2

O,O-Diethyl O-pyrazinyl phosphorothioate

ON1046

P085

152-16-9

Octamethylpyrophosphoramide

ON1057

P087

20816-12-0

Osmium oxide OsO4,(T-4)-

ON1090

P087

20816-12-0

Osmium tetroxide

ON1090

P194

23135-22-0

Oxamyl

 

P089

56-38-2

Parathion

ON1091

P024

106-47-8

p-Chloroaniline

ON1022

P020

88-85-7

Phenol, 2-(1-methylpropyl)-4,6-dinitro-

ON1056

P009

131-74-8

Phenol, 2,4,6-trinitro-, ammonium salt

ON1015

P048

51-28-5

Phenol, 2,4-dinitro-

ON1055

P034

131-89-5

Phenol, 2-cyclohexyl-4,6-dinitro-

ON1054

P047

**534-52-1

Phenol, 2-methyl-4,6-dinitro-, & salts

ON1053

P202

64-00-6

Phenol, 3-(1-methylethyl)-, methyl carbamate

 

P201

2631-37-0

Phenol, 3-methyl-5-(1-methylethyl)-,methyl carbamate

 

P199

2032-65-7

Phenol,(3,5-dimethyl-4-(methylthio)-,methylcarbamate

 

P128

315-18-4

Phenol,4-(dimethylamino)-3,5-dimethyl-, methylcarbamate (ester)

 

P092

62-38-4

Phenylmercury acetate

ON1079

P093

103-85-5

Phenylthiourea

ON1092

P094

298-02-2

Phorate

ON1093

P095

75-44-5

Phosgene

ON1035

P096

7803-51-2

Phosphine

ON1077

P041

311-45-5

Phosphoric acid, diethyl 4-nitrophenyl ester

ON1045

P094

298-02-2

Phosphorodithioic acid, O,O-diethyl S-[(ethylthio)methyl] ester

ON1093

P039

298-04-4

Phosphorodithioic acid, O,O-diethyl S-[2-(ethylthio)ethyl] ester

ON1044

P044

60-51-5

Phosphorodithioic acid,O,O-dimethylS-[2-(methylamino)-2-oxoethyl] ester

ON1048

P043

55-91-4

Phosphorofluoridic acid, bis(1-methylethyl) ester

ON1047

P071

298-00-0

Phosphorothioic acid, O,O,-dimethyl O-(4-nitrophenyl) ester

ON1050

P089

56-38-2

Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester

ON1091

P040

297-97-2

Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester

ON1046

P097

52-85-7

Phosphorothioic acid, O-[4-[(dimethylamino)sulfonyl]phenyl] O,O-r dimethyl ester

ON1065

P188

57-64-7

Physostigmine salicylate.

 

P204

57-47-6

Physostigmine.

 

P110

78-00-2

Plumbane, tetraethyl-

ON1094

P077

100-01-6

p-Nitroaniline

ON1023

P098

151-50-8

Potassium cyanide

ON1095

P098

151-50-8

Potassium cyanide K(CN)

ON1095

P099

506-61-6

Potassium silver cyanide

ON1096

P201

2631-37-0

Promecarb

 

P203

1646-88-4

Propanal,2-methyl-2-(methyl-sulfonyl)-,O-[(methylamino)carbonyl] oxime

 

P070

116-06-3

Propanal,2-methyl-2-(methylthio)-,O-[(methylamino)carbonyl]oxime

ON1009

P101

107-12-0

Propanenitrile

ON1064

P069

75-86-5

Propanenitrile, 2-hydroxy-2-methyl-

ON1005

P027

542-76-7

Propanenitrile, 3-chloro-

ON1038

P102

107-19-7

Propargyl alcohol

ON1097

P075

**54-11-5

Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)-, & salts

ON1086

P204

57-47-6

Pyrrolo[2,3-b]indol-5-ol,1,2,3,3a,8,8a-hexahydro-1,3a,8- trimethyl-,methylcarbamate (ester),
(3aS-cis)-

 

P114

12039-52-0

Selenious acid, dithallium(1+) salt

ON1106

P103

630-10-4

Selenourea

ON1033

P104

506-64-9

Silver cyanide

ON1099

P104

506-64-9

Silver cyanide Ag(CN)

ON1099

P105

26628-22-8

Sodium azide

ON1100

P106

143-33-9

Sodium cyanide

ON1101

P106

143-33-9

Sodium cyanide Na(CN)

ON1101

P108

**57-24-9

Strychnidin-10-one, & salts

ON1103

P018

357-57-3

Strychnidin-10-one, 2,3-dimethoxy-

ON1030

P108

**57-24-9

Strychnine, & salts

ON1103

P115

7446-18-6

Sulfuric acid, dithallium(1+) salt

ON1105

P110

78-00-2

Tetraethyl lead

ON1094

P111

107-49-3

Tetraethyl pyrophosphate

ON1098

P109

3689-24-5

Tetraethyldithiopyrophosphate

ON1059

P112

509-14-8

Tetranitromethane

ON1080

P062

757-58-4

Tetraphosphoric acid, hexaethyl ester

ON1072

P113

1314-32-5

Thallic oxide

ON1104

P113

1314-32-5

Thallium oxide Tl2O3

ON1104

P114

12039-52-0

Thallium(I) selenite

ON1106

P115

7446-18-6

Thallium(I) sulfate

ON1105

P109

3689-24-5

Thiodiphosphoric acid, tetraethyl ester

ON1059

P045

39196-18-4

Thiofanox

ON1049

P049

541-53-7

Thioimidodicarbonic diamide [(H2N)C(S)]2NH

ON1058

P014

108-98-5

Thiophenol

ON1026

P116

79-19-6

Thiosemicarbazide

ON1073

P026

5344-82-1

Thiourea, (2-chlorophenyl)-

ON1037

P072

86-88-4

Thiourea, 1-naphthalenyl-

ON1083

P093

103-85-5

Thiourea, phenyl-

ON1092

P185

26419-73-8

Tirpate

 

P123

8001-35-2

Toxaphene

ON1032

P118

75-70-7

Trichloromethanethiol

ON1081

P119

7803-55-6

Vanadic acid, ammonium salt

ON1014

P120

1314-62-1

Vanadium oxide V2O5

ON1107

P120

1314-62-1

Vanadium pentoxide

ON1107

P084

4549-40-0

Vinylamine, N-methyl-N-nitroso-

ON1063

P001

**81-81-2

Warfarin, & salts, when present at concentrations greater than 0.3%

ON1006

P121

557-21-1

Zinc cyanide

ON1108

P121

557-21-1

Zinc cyanide Zn(CN)2

ON1108

P122

1314-84-7

Zinc phosphide Zn3P2, when present at concentrations greater than 10%

ON1109

P205

137-30-4

Zinc, bis(dimethylcarbamodithioato-S,S')-,

 

P205

137-30-4

Ziram

 

 

schedule 2
Part B — Hazardous Waste Chemicals

Hazardous Waste No.

Chemical Abstracts No.

Substance

Reference Number

U021

92-87-5

[1,1-Biphenyl]-4,4-diamine

ON2064

U073

91-94-1

[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dichloro-

ON2071

U091

119-90-4

[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethoxy-

ON2072

U095

119-93-7

[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethyl-

ON2073

U208

630-20-6

1,1,1,2-Tetrachloroethane

ON2158

U209

79-34-5

1,1,2,2-Tetrachloroethane

ON2159

U227

79-00-5

1,1,2-Trichloroethane

ON2162

U078

75-35-4

1,1-Dichloroethylene

ON2128

U098

57-14-7

1,1-Dimethylhydrazine

ON2144

U207

95-94-3

1,2,4,5-Tetrachlorobenzene

ON2061

U085

1464-53-5

1,2:3,4-Diepoxybutane

ON2070

U069

84-74-2

1,2-Benzenedicarboxylic acid, dibutyl ester

ON2037

U088

84-66-2

1,2-Benzenedicarboxylic acid, diethyl ester

ON2038

U102

131-11-3

1,2-Benzenedicarboxylic acid, dimethyl ester

ON2039

U107

117-84-0

1,2-Benzenedicarboxylic acid, dioctyl ester

ON2040

U028

117-81-7

1,2-Benzenedicarboxylic acid,bis(2-ethylhexyl) ester

ON2036

U202

**81-07-2

1,2-Benzisothiazol-3(2H)-one, 1,1-dioxide, & salts

ON2065

U066

96-12-8

1,2-Dibromo-3-chloropropane

ON2124

U079

156-60-5

1,2-Dichloroethylene

ON2129

U099

540-73-8

1,2-Dimethylhydrazine

ON2145

U109

122-66-7

1,2-Diphenylhydrazine

ON2148

U155

91-80-5

1,2-Ethanediamine,N,N-dimethyl-N'-2-pyridinyl-N'-(2-thienylmethyl)-

ON2202

U193

1120-71-4

1,2-Oxathiolane, 2,2-dioxide

ON2216

U142

143-50-0

1,3,4-Metheno-2H-cyclobuta[cd]pentalen-2-one, 1,1a,3,3a,4,5,5,5a,5b,6-decachlorooctahydro-

ON2118

U234

99-35-4

1,3,5-Trinitrobenzene

ON2063

U182

123-63-7

1,3,5-Trioxane, 2,4,6-trimethyl-

ON2217

U201

108-46-3

1,3-Benzenediol

ON2046

U364

22961-82-6

1,3-Benzodioxol-4-ol, 2,2-dimethyl-,

 

U278

22781-23-3

1,3-Benzodioxol-4-ol, 2,2-dimethyl-,methyl carbamate

 

U141

120-58-1

1,3-Benzodioxole, 5-(1-propenyl)-

ON2054

U203

94-59-7

1,3-Benzodioxole, 5-(2-propenyl)-

ON2053

U090

94-58-6

1,3-Benzodioxole, 5-propyl-

ON2055

U128

87-68-3

1,3-Butadiene, 1,1,2,3,4,4-hexachloro-

ON2079

U130

77-47-4

1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro-

ON2112

U084

542-75-6

1,3-Dichloropropene

ON2135

U190

85-44-9

1,3-Isobenzofurandione

ON2035

U186

504-60-9

1,3-Pentadiene

ON2203

U193

1120-71-4

1,3-Propane sultone

ON2216

U074

764-41-0

1,4-Dichloro-2-butene

ON2086

U108

123-91-1

1,4-Diethyleneoxide

ON2136

U108

123-91-1

1,4-Dioxane

ON2136

U166

130-15-4

1,4-Naphthalenedione

ON2208

U166

130-15-4

1,4-Naphthoquinone

ON2208

U172

924-16-3

1-Butanamine, N-butyl-N-nitroso-

ON2080

U031

71-36-3

1-Butanol

ON2082

U011

61-82-5

1H-1,2,4-Triazol-3-amine

ON2016

U186

504-60-9

1-Methylbutadiene

ON2203

U167

134-32-7

1-Naphthalenamine

ON2210

U279

63-25-2

1-Naphthalenol, methylcarbamate

 

U194

107-10-8

1-Propanamine

ON2224

U111

621-64-7

1-Propanamine, N-nitroso-N-propyl-

ON2150

U110

142-84-7

1-Propanamine, N-propyl-

ON2149

U235

126-72-7

1-Propanol, 2,3-dibromo-, phosphate (3:1)

ON2225

U140

78-83-1

1-Propanol, 2-methyl-

ON2189

U243

1888-71-7

1-Propene, 1,1,2,3,3,3-hexachloro-

ON2184

U084

542-75-6

1-Propene, 1,3-dichloro-

ON2135

U085

1464-53-5

2,2-Bioxirane

ON2070

F027

58-90-2

2,3,4,6-Tetrachlorophenol

ON2219

U237

66-75-1

2,4-(1H,3H)-Pyrimidinedione, 5-[bis(2-chloroethyl)amino]-

ON2237

F027

93-76-5

2,4,5-T

ON2233

F027

95-95-4

2,4,5-Trichlorophenol

ON2220

U408

118-79-6

2,4,6-Tribromophenol

 

F027

88-06-2

2,4,6-Trichlorophenol

ON2221

U240

**94-75-7

2,4-D, salts & esters

ON2114

U081

120-83-2

2,4-Dichlorophenol

ON2132

U101

105-67-9

2,4-Dimethylphenol

ON2146

U105

121-14-2

2,4-Dinitrotoluene

ON2051

U197

106-51-4

2,5-Cyclohexadiene-1,4-dione

ON2068

U147

108-31-6

2,5-Furandione

ON2177

U082

87-65-0

2,6-Dichlorophenol

ON2133

U106

606-20-2

2,6-Dinitrotoluene

ON2052

U236

72-57-1

2,7-Naphthalenedisulfonic acid, 3,3'-[(3,3'-dimethyl[1,1'-biphenyl]-4,4'-diyl)bis(azo)bis[5-amino-4-hydroxy]-,tetrasodium salt

ON2209

U005

53-96-3

2-Acetylaminofluorene

ON2004

U159

78-93-3

2-Butanone

ON2083

U160

1338-23-4

2-Butanone, peroxide

ON2084

U053

4170-30-3

2-Butenal

ON2085

U074

764-41-0

2-Butene, 1,4-dichloro-

ON2086

U143

303-34-4

2-Butenoic acid, 2-methyl-, 7-[[2,3-dihydroxy-2-(1-methoxyethyl)-3-methyl-1-oxobutoxy]methyl]-2,3,5,7a-tetrahydro-1H-pyrrolizin-1-yl ester,[1S-[1alpha(Z),7(2S*,3R*), 7aalpha]]-

ON2190

U042

110-75-8

2-Chloroethyl vinyl ether

ON2103

U125

98-01-1

2-Furancarboxaldehyde

ON2176

U058

50-18-0

2H-1,3,2-Oxazaphosphorin-2-amine,N,N-bis(2-chloroethyl)tetrahydro-, 2-oxide

ON2113

U248

**81-81-2

2H-1-Benzopyran-2-one,4-hydroxy-3-(3-oxo-1-phenyl-butyl)-, & salts, when present at concentrations of 0.3% or less

ON2009

U116

96-45-7

2-Imidazolidinethione

ON2169

U168

91-59-8

2-Naphthalenamine

ON2211

U171

79-46-9

2-Nitropropane

ON2213

U191

109-06-8

2-Picoline

ON2223

U002

67-64-1

2-Propanone

ON2226

U007

79-06-1

2-Propenamide

ON2012

U009

107-13-1

2-Propenenitrile

ON2014

U152

126-98-7

2-Propenenitrile, 2-methyl-

ON2195

U008

79-10-7

2-Propenoic acid

ON2013

U118

97-63-2

2-Propenoic acid, 2-methyl-, ethyl ester

ON2170

U162

80-62-6

2-Propenoic acid, 2-methyl-, methyl ester

ON2205

U113

140-88-5

2-Propenoic acid, ethyl ester

ON2167

U073

91-94-1

3,3'-Dichlorobenzidine

ON2071

U091

119-90-4

3,3'-Dimethoxybenzidine

ON2072

U095

119-93-7

3,3'-Dimethylbenzidine

ON2073

U148

123-33-1

3,6-Pyridazinedione, 1,2-dihydro-

ON2141

U157

56-49-5

3-Methylcholanthrene

ON2021

U164

56-04-2

4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo-

ON2206

U158

101-14-4

4,4'-Methylenebis(2-chloroaniline)

ON2028

U036

57-74-9

4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro-

ON2099

U030

101-55-3

4-Bromophenyl phenyl ether

ON2033

U049

3165-93-3

4-Chloro-o-toluidine, hydrochloride

ON2026

U161

108-10-1

4-Methyl-2-pentanone

ON2204

U059

20830-81-3

5,12-Naphthacenedione,8-acetyl-10-[(3-amino-2,3,6-trideoxy)-alpha-L-lyxo-hexopyranosyl)oxy]-7,8,9,10-tetrahydro-6,8,11-trihydroxy-1-methoxy-, (8S-cis)-

ON2115

U181

99-55-8

5-Nitro-o-toluidine

ON2030

U094

57-97-6

7,12-Dimethylbenz[a]anthracene

ON2025

U367

1563-38-8

7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-

 

U394

30558-43-1

A2213

 

U001

75-07-0

Acetaldehyde

ON2001

U034

75-87-6

Acetaldehyde, trichloro-

ON2002

U187

62-44-2

Acetamide, N-(4-ethoxyphenyl)-

ON2003

U005

53-96-3

Acetamide, N-9H-fluoren-2-yl-

ON2004

U112

141-78-6

Acetic acid ethyl ester

ON2005

See F027

93-76-5

Acetic acid, (2,4,5-trichlorophenoxy)-

ON2233

U240

**94-75-7

Acetic acid, (2,4-dichlorophenoxy)-,salts & esters

ON2114

U144

301-04-2

Acetic acid, lead(2+) salt

ON2006

U214

563-68-8

Acetic acid, thallium(1+) salt

ON2007

U002

67-64-1

Acetone

ON2226

U003

75-05-8

Acetonitrile

ON2008

U004

98-86-2

Acetophenone

ON2010

U006

75-36-5

Acetyl chloride

ON2011

U007

79-06-1

Acrylamide

ON2012

U008

79-10-7

Acrylic acid

ON2013

U009

107-13-1

Acrylonitrile

ON2014

U096

80-15-9

alpha,alpha-Dimethylbenzylhydroperoxide

ON2143

U167

134-32-7

alpha-Naphthylamine

ON2210

U011

61-82-5

Amitrole

ON2016

U012

62-53-3

Aniline

ON2017

U136

75-60-5

Arsinic acid, dimethyl-

ON2087

U014

492-80-8

Auramine

ON2018

U015

115-02-6

Azaserine

ON2019

U010

50-07-7

Azirino[2,3_3,4]pyrrolo[1,2-a]indole-4,7-dione,6-amino-8-[[(aminocarbonyl)oxy]methyl]-1,1a,2,8,8a,8b-hexahydro-8a-methoxy-5-methyl-, [1aS-(1aalpha,8beta,8aalpha,8balpha)]-

ON2020

U280

101-27-9

Barban.

 

U364

22961-82-6

Bendiocarb phenol

 

U278

22781-23-3

Bendiocarb.

 

U271

17804-35-2

Benomyl.

 

U018

56-55-3

Benz[a]anthracene

ON2024

U094

57-97-6

Benz[a]anthracene, 7,12-dimethyl-

ON2025

U016

225-51-4

Benz[c]acridine

ON2022

U157

56-49-5

Benz[j]aceanthrylene, 1,2-dihydro-3-methyl-

ON2021

U017

98-87-3

Benzal chloride

ON2023

U192

23950-58-5

Benzamide,3,5-dichloro-N-(1,1-dimethyl-2-propynyl)-

ON2127

U012

62-53-3

Benzenamine

ON2017

U328

95-53-4

Benzenamine, 2-methyl-

 

U222

636-21-5

Benzenamine, 2-methyl-, hydrochloride

ON2029

U181

99-55-8

Benzenamine, 2-methyl-5-nitro-

ON2030

U014

492-80-8

Benzenamine, 4,4-carbonimidoylbis[N,N-dimethyl-

ON2018

U158

101-14-4

Benzenamine, 4,4-methylenebis[2-chloro-

ON2028

U049

3165-93-3

Benzenamine, 4-chloro-2-methyl-,hydrochloride

ON2026

U353

106-49-0

Benzenamine, 4-methyl-

 

U093

60-11-7

Benzenamine, N,N-dimethyl-4-(phenylazo)-

ON2027

U019

71-43-2

Benzene

ON2031

U055

98-82-8

Benzene, (1-methylethyl)-

ON2056

U017

98-87-3

Benzene, (dichloromethyl)-

ON2023

U023

98-07-7

Benzene, (trichloromethyl)-

ON2062

U247

72-43-5

Benzene, 1,1-(2,2,2-trichloroethylidene)bis[4- methoxy-

ON2163

U207

95-94-3

Benzene, 1,2,4,5-tetrachloro-

ON2061

U070

95-50-1

Benzene, 1,2-dichloro-

ON2041

U234

99-35-4

Benzene, 1,3,5-trinitro-

ON2063

U071

541-73-1

Benzene, 1,3-dichloro-

ON2042

U223

26471-62-5

Benzene, 1,3-diisocyanatomethyl-

ON2044

U072

106-46-7

Benzene, 1,4-dichloro-

ON2043

U030

101-55-3

Benzene, 1-bromo-4-phenoxy-

ON2033

U105

121-14-2

Benzene, 1-methyl-2,4-dinitro-

ON2051

U106

606-20-2

Benzene, 2-methyl-1,3-dinitro-

ON2052

U037

108-90-7

Benzene, chloro-

ON2034

U239

1330-20-7

Benzene, dimethyl-

ON2045

U127

118-74-1

Benzene, hexachloro-

ON2047

U056

110-82-7

Benzene, hexahydro-

ON2048

U220

108-88-3

Benzene, methyl-

ON2050

U169

98-95-3

Benzene, nitro-

ON2057

U183

608-93-5

Benzene, pentachloro-

ON2058

U185

82-68-8

Benzene, pentachloronitro-

ON2059

U061

50-29-3

Benzene,1,1-(2,2,2-trichloroethylidene)bis[4-chloro-

ON2117

U060

72-54-8

Benzene,1,1-(2,2-dichloroethylidene)bis[4-chloro-

ON2116

U038

510-15-6

Benzeneacetic acid,4-chloro-alpha- (4-chlorophenyl)-alpha-hydroxy-, ethyl ester

ON2032

U035

305-03-3

Benzenebutanoic acid, 4-[bis(2-chloroethyl)amino]-

ON2081

U221

25376-45-8

Benzenediamine, ar-methyl-

ON2121

U020

98-09-9

Benzenesulfonic acid chloride

ON2060

U020

98-09-9

Benzenesulfonyl chloride

ON2060

U021

92-87-5

Benzidine

ON2064

U022

50-32-8

Benzo[a]pyrene

ON2067

U064

189-55-9

Benzo[rst]pentaphene

ON2123

U023

98-07-7

Benzotrichloride

ON2062

U047

91-58-7

beta-Chloronaphthalene

ON2106

U168

91-59-8

beta-Naphthylamine

ON2211

U225

75-25-2

Bromoform

ON2078

U136

75-60-5

Cacodylic acid

ON2087

U032

13765-19-0

Calcium chromate

ON2088

U280

101-27-9

Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester

 

U409

23564-05-8

Carbamic acid, [1,2-phenylenebis (iminocarbonothioyl)]bis-, dimethyl ester

 

U271

17804-35-2

Carbamic acid, [1-[(butylamino)carbonyl]-1H-benzimidazol-2-yl]-, methyl ester

 

U372

10605-21-7

Carbamic acid, 1H-benzimidazol-2-yl,methyl ester

 

U238

51-79-6

Carbamic acid, ethyl ester

ON2089

U178

615-53-2

Carbamic acid, methylnitroso-, ethyl ester

ON2090

U373

122-42-9

Carbamic acid, phenyl-, 1-methylethyl ester

 

U097

79-44-7

Carbamic chloride, dimethyl-

ON2094

U114

**111-54-6

Carbamodithioic acid, 1,2-ethanediylbis-,salts & esters

ON2155

U389

2303-17-5

Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl)ester

 

U062

2303-16-4

Carbamothioic acid, bis(1-methylethyl)-S-(2,3-dichloro-2-propenyl) ester

ON2119

U387

52888-80-9

Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester

 

U279

63-25-2

Carbaryl.

 

U372

10605-21-7

Carbendazim

 

U367

1563-38-8

Carbofuran phenol

 

U033

353-50-4

Carbon oxyfluoride

ON2097

U211

56-23-5

Carbon tetrachloride

ON2098

U215

6533-73-9

Carbonic acid, dithallium(1+) salt

ON2095

U033

353-50-4

Carbonic difluoride

ON2097

U156

79-22-1

Carbonochloridic acid, methyl ester

ON2096

U034

75-87-6

Chloral

ON2002

U035

305-03-3

Chlorambucil

ON2081

U036

57-74-9

Chlordane, alpha & gamma isomers

ON2099

U026

494-03-1

Chlornaphazin

ON2100

U037

108-90-7

Chlorobenzene

ON2034

U038

510-15-6

Chlorobenzilate

ON2032

U044

67-66-3

Chloroform

ON2104

U046

107-30-2

Chloromethyl methyl ether

ON2105

U032

13765-19-0

Chromic acid H2CrO4, calcium salt

ON2088

U050

218-01-9

Chrysene

ON2069

U051

N/A

Creosote

ON2108

U052

1319-77-3

Cresol (Cresylic acid)

ON2109

U053

4170-30-3

Crotonaldehyde

ON2085

U055

98-82-8

Cumene

ON2056

U246

506-68-3

Cyanogen bromide (CN)Br

ON2077

U056

110-82-7

Cyclohexane

ON2048

U129

58-89-9

Cyclohexane, 1,2,3,4,5,6-hexachloro-,(1alpha,2alpha,3beta,4alpha,5alpha,6 beta)-

ON2182

U057

108-94-1

Cyclohexanone

ON2111

U058

50-18-0

Cyclophosphamide

ON2113

U059

20830-81-3

Daunomycin

ON2115

U060

72-54-8

DDD

ON2116

U061

50-29-3

DDT

ON2117

U206

18883-66-4

D-Glucose,2-deoxy-2-[[(methylnitrosoamino)-carbonyl]amino]-

ON2179

U062

2303-16-4

Diallate

ON2119

U063

53-70-3

Dibenz[a,h]anthracene

ON2122

U064

189-55-9

Dibenzo[a,i]pyrene

ON2123

U069

84-74-2

Dibutyl phthalate

ON2037

U075

75-71-8

Dichlorodifluoromethane

ON2126

U025

111-44-4

Dichloroethyl ether

ON2130

U027

108-60-1

Dichloroisopropyl ether

ON2075

U024

111-91-1

Dichloromethoxy ethane

ON2074

U088

84-66-2

Diethyl phthalate

ON2038

U395

5952-26-1

Diethylene glycol, dicarbamate

 

U028

117-81-7

Diethylhexyl phthalate

ON2036

U089

56-53-1

Diethylstilbesterol

ON2140

U090

94-58-6

Dihydrosafrole

ON2055

U102

131-11-3

Dimethyl phthalate

ON2039

U103

77-78-1

Dimethyl sulfate

ON2147

U092

124-40-3

Dimethylamine

ON2142

U097

79-44-7

Dimethylcarbamoyl chloride

ON2094

U107

117-84-0

Di-n-octyl phthalate

ON2040

U111

621-64-7

Di-n-propylnitrosamine

ON2150

U110

142-84-7

Dipropylamine

ON2149

U041

106-89-8

Epichlorohydrin

ON2102

U001

75-07-0

Ethanal

ON2001

U404

121-44-8

Ethanamine, N,N-diethyl-

 

U174

55-18-5

Ethanamine, N-ethyl-N-nitroso-

ON2151

U208

630-20-6

Ethane, 1,1,1,2-tetrachloro-

ON2158

U226

71-55-6

Ethane, 1,1,1-trichloro-

ON2161

U209

79-34-5

Ethane, 1,1,2,2-tetrachloro-

ON2159

U227

79-00-5

Ethane, 1,1,2-trichloro-

ON2162

U024

111-91-1

Ethane, 1,1'-[methylenebis(oxy)]bis[2-chloro-

ON2074

U076

75-34-3

Ethane, 1,1-dichloro-

ON2153

U117

60-29-7

Ethane, 1,1'-oxybis-

ON2137

U025

111-44-4

Ethane, 1,1'-oxybis[2-chloro-

ON2130

U067

106-93-4

Ethane, 1,2-dibromo-

ON2152

U077

107-06-2

Ethane, 1,2-dichloro-

ON2154

U131

67-72-1

Ethane, hexachloro-

ON2156

U184

76-01-7

Ethane, pentachloro-

ON2157

U218

62-55-5

Ethanethioamide

ON2160

U394

30558-43-1

Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-,methyl ester

 

U410

59669-26-0

Ethanimidothioic acid, N,N'-[thiobis[(methylimino)carbonyloxy]]bi s-, dimethyl ester

 

U173

1116-54-7

Ethanol, 2,2'-(nitrosoimino)bis-

ON2164

U395

5952-26-1

Ethanol, 2,2'-oxybis-, dicarbamate

 

U359

110-80-5

Ethanol, 2-ethoxy-

ON2239

U004

98-86-2

Ethanone, 1-phenyl-

ON2010

U042

110-75-8

Ethene, (2-chloroethoxy)-

ON2103

U078

75-35-4

Ethene, 1,1-dichloro-

ON2128

U079

156-60-5

Ethene, 1,2-dichloro-, (E)-

ON2129

U043

75-01-4

Ethene, chloro-

ON2165

U210

127-18-4

Ethene, tetrachloro-

ON2166

U228

79-01-6

Ethene, trichloro-

ON2236

U112

141-78-6

Ethyl acetate

ON2005

U113

140-88-5

Ethyl acrylate

ON2167

U238

51-79-6

Ethyl carbamate (urethane)

ON2089

U117

60-29-7

Ethyl ether

ON2137

U118

97-63-2

Ethyl methacrylate

ON2170

U119

62-50-0

Ethyl methanesulfonate

ON2171

U067

106-93-4

Ethylene dibromide

ON2152

U077

107-06-2

Ethylene dichloride

ON2154

U359

110-80-5

Ethylene glycol monoethyl ether

ON2239

U115

75-21-8

Ethylene oxide

ON2168

U114

**111-54-6

Ethylenebisdithiocarbamic acid, salts & esters

ON2155

U116

96-45-7

Ethylenethiourea

ON2169

U076

75-34-3

Ethylidene dichloride

ON2153

U120

206-44-0

Fluoranthene

ON2066

U122

50-00-0

Formaldehyde

ON2173

U123

64-18-6

Formic acid

ON2174

U124

110-00-9

Furan

ON2175

U213

109-99-9

Furan, tetrahydro-

ON2178

U125

98-01-1

Furfural

ON2176

U124

110-00-9

Furfuran

ON2175

U206

18883-66-4

Glucopyranose,2-deoxy-2-(3-methyl-3-nitrosoureido)-, D-

ON2179

U126

765-34-4

Glycidylaldehyde

ON2180

U163

70-25-7

Guanidine, N-methyl-N'-nitro-N-nitroso-

ON2181

U127

118-74-1

Hexachlorobenzene

ON2047

U128

87-68-3

Hexachlorobutadiene

ON2079

U130

77-47-4

Hexachlorocyclopentadiene

ON2112

U131

67-72-1

Hexachloroethane

ON2156

U132

70-30-4

Hexachlorophene

ON2183

U243

1888-71-7

Hexachloropropene

ON2184

U133

302-01-2

Hydrazine

ON2120

U098

57-14-7

Hydrazine, 1,1-dimethyl-

ON2144

U086

1615-80-1

Hydrazine, 1,2-diethyl-

ON2138

U099

540-73-8

Hydrazine, 1,2-dimethyl-

ON2145

U109

122-66-7

Hydrazine, 1,2-diphenyl-

ON2148

U134

7664-39-3

Hydrofluoric acid

ON2185

U134

7664-39-3

Hydrogen fluoride

ON2185

U135

7783-06-4

Hydrogen sulfide

ON2187

U135

7783-06-4

Hydrogen sulfide H2S

ON2187

U096

80-15-9

Hydroperoxide, 1-methyl-1-phenylethyl-

ON2143

U137

193-39-5

Indeno[1,2,3-cd]pyrene

ON2188

U140

78-83-1

Isobutyl alcohol

ON2189

U141

120-58-1

Isosafrole

ON2054

U142

143-50-0

Kepone

ON2118

U143

303-34-4

Lasiocarpine

ON2190

U144

301-04-2

Lead acetate

ON2006

U145

7446-27-7

Lead phosphate

ON2191

U146

1335-32-6

Lead subacetate

ON2192

U146

1335-32-6

Lead, bis(acetato-O)tetrahydroxytri-

ON2192

U129

58-89-9

Lindane

ON2182

U150

148-82-3

L-Phenylalanine, 4-[bis(2-chloroethyl)amino]-

ON2015

U015

115-02-6

L-Serine, diazoacetate (ester)

ON2019

U147

108-31-6

Maleic anhydride

ON2177

U148

123-33-1

Maleic hydrazide

ON2141

U149

109-77-3

Malononitrile

ON2193

U071

541-73-1

m-Dichlorobenzene

ON2042

U150

148-82-3

Melphalan

ON2015

U151

7439-97-6

Mercury

ON2194

U152

126-98-7

Methacrylonitrile

ON2195

U092

124-40-3

Methanamine, N-methyl-

ON2142

U029

74-83-9

Methane, bromo-

ON2196

U045

74-87-3

Methane, chloro-

ON2197

U046

107-30-2

Methane, chloromethoxy-

ON2105

U068

74-95-3

Methane, dibromo-

ON2125

U080

75-09-2

Methane, dichloro-

ON2131

U075

75-71-8

Methane, dichlorodifluoro-

ON2126

U138

74-88-4

Methane, iodo-

ON2198

U211

56-23-5

Methane, tetrachloro-

ON2098

U225

75-25-2

Methane, tribromo-

ON2078

U044

67-66-3

Methane, trichloro-

ON2104

U121

75-69-4

Methane, trichlorofluoro-

ON2200

U119

62-50-0

Methanesulfonic acid, ethyl ester

ON2171

U153

74-93-1

Methanethiol

ON2199

U154

67-56-1

Methanol

ON2201

U155

91-80-5

Methapyrilene

ON2202

U247

72-43-5

Methoxychlor

ON2163

U154

67-56-1

Methyl alcohol

ON2201

U029

74-83-9

Methyl bromide

ON2196

U045

74-87-3

Methyl chloride

ON2197

U156

79-22-1

Methyl chlorocarbonate

ON2096

U226

71-55-6

Methyl chloroform

ON2161

U159

78-93-3

Methyl ethyl ketone (MEK)

ON2083

U160

1338-23-4

Methyl ethyl ketone peroxide

ON2084

U138

74-88-4

Methyl iodide

ON2198

U161

108-10-1

Methyl isobutyl ketone

ON2204

U162

80-62-6

Methyl methacrylate

ON2205

U068

74-95-3

Methylene bromide

ON2125

U080

75-09-2

Methylene chloride

ON2131

U164

56-04-2

Methylthiouracil

ON2206

U010

50-07-7

Mitomycin C

ON2020

U163

70-25-7

MNNG

ON2181

U086

1615-80-1

N,N'-Diethylhydrazine

ON2138

U026

494-03-1

Naphthalenamine, N,N'-bis(2-chloroethyl)-

ON2100

U165

91-20-3

Naphthalene

ON2207

U047

91-58-7

Naphthalene, 2-chloro-

ON2106

U031

71-36-3

n-Butyl alcohol

ON2082

U217

10102-45-1

Nitric acid, thallium(1+) salt

ON2235

U169

98-95-3

Nitrobenzene

ON2057

U173

1116-54-7

N-Nitrosodiethanolamine

ON2164

U174

55-18-5

N-Nitrosodiethylamine

ON2151

U172

924-16-3

N-Nitrosodi-n-butylamine

ON2080

U176

759-73-9

N-Nitroso-N-ethylurea

ON2091

U177

684-93-5

N-Nitroso-N-methylurea

ON2092

U178

615-53-2

N-Nitroso-N-methylurethane

ON2090

U179

100-75-4

N-Nitrosopiperidine

ON2214

U180

930-55-2

N-Nitrosopyrrolidine

ON2215

U194

107-10-8

n-Propylamine

ON2224

U087

3288-58-2

O,O-Diethyl S-methyl dithiophosphate

ON2139

U048

95-57-8

o-Chlorophenol

ON2107

U070

95-50-1

o-Dichlorobenzene

ON2041

U328

95-53-4

o-Toluidine

 

U222

636-21-5

o-Toluidine hydrochloride

ON2029

U115

75-21-8

Oxirane

ON2168

U041

106-89-8

Oxirane, (chloromethyl)-

ON2102

U126

765-34-4

Oxiranecarboxyaldehyde

ON2180

U182

123-63-7

Paraldehyde

ON2217

U197

106-51-4

p-Benzoquinone

ON2068

U039

59-50-7

p-Chloro-m-cresol

ON2101

U072

106-46-7

p-Dichlorobenzene

ON2043

U093

60-11-7

p-Dimethylaminoazobenzene

ON2027

U183

608-93-5

Pentachlorobenzene

ON2058

U184

76-01-7

Pentachloroethane

ON2157

U185

82-68-8

Pentachloronitrobenzene (PCNB)

ON2059

F027

87-86-5

Pentachlorophenol

ON2218

U161

108-10-1

Pentanol, 4-methyl-

ON2204

U187

62-44-2

Phenacetin

ON2003

U188

108-95-2

Phenol

ON2049

U411

114-26-1

Phenol, 2-(1-methylethoxy)-,methylcarbamate

 

F027

58-90-2

Phenol, 2,3,4,6-tetrachloro-

ON2219

F027

95-95-4

Phenol, 2,4,5-trichloro-

ON2220

F027

88-06-2

Phenol, 2,4,6-trichloro-

ON2221

U081

120-83-2

Phenol, 2,4-dichloro-

ON2132

U101

105-67-9

Phenol, 2,4-dimethyl-

ON2146

U082

87-65-0

Phenol, 2,6-dichloro-

ON2133

U048

95-57-8

Phenol, 2-chloro-

ON2107

U089

56-53-1

Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)-

ON2140

U039

59-50-7

Phenol, 4-chloro-3-methyl-

ON2101

U170

100-02-7

Phenol, 4-nitro-

ON2212

U052

1319-77-3

Phenol, methyl-

ON2109

F027

87-86-5

Phenol, pentachloro-

ON2218

U132

70-30-4

Phenol,2,2'-methylenebis[3,4,6-trichloro-

ON2183

U145

7446-27-7

Phosphoric acid, lead(2+) salt (2:3)

ON2191

U087

3288-58-2

Phosphorodithioic acid, O,O-diethyl S-methyl ester

ON2139

U189

1314-80-3

Phosphorus sulfide

ON2222

U190

85-44-9

Phthalic anhydride

ON2035

U179

100-75-4

Piperidine, 1-nitroso-

ON2214

U170

100-02-7

p-Nitrophenol

ON2212

U192

23950-58-5

Pronamide

ON2127

U066

96-12-8

Propane, 1,2-dibromo-3-chloro-

ON2124

U083

78-87-5

Propane, 1,2-dichloro-

ON2134

U027

108-60-1

Propane, 2,2'-oxybis[2-chloro-

ON2075

U171

79-46-9

Propane, 2-nitro-

ON2213

U149

109-77-3

Propanedinitrile

ON2193

F027

93-72-1

Propanoic acid, 2-(2,4,5-0 trichlorophenoxy)-

ON2227

U373

122-42-9

Propham

 

U411

114-26-1

Propoxur.

 

U083

78-87-5

Propylene dichloride

ON2134

U387

52888-80-9

Prosulfocarb

 

U353

106-49-0

p-Toluidine

 

U196

110-86-1

Pyridine

ON2228

U191

109-06-8

Pyridine, 2-methyl-

ON2223

U180

930-55-2

Pyrrolidine, 1-nitroso-

ON2215

U200

50-55-5

Reserpine

ON2229

U201

108-46-3

Resorcinol

ON2046

U202

**81-07-2

Saccharin, & salts

ON2065

U203

94-59-7

Safrole

ON2053

U204

7783-00-8

Selenious acid

ON2230

U204

7783-00-8

Selenium dioxide

ON2230

U205

7488-56-4

Selenium sulfide

ON2232

U205

7488-56-4

Selenium sulfide SeS2

ON2232

F027

93-72-1

Silvex (2,4,5-TP)

ON2227

U206

18883-66-4

Streptozotocin

ON2179

U189

1314-80-3

Sulfur phosphide

ON2222

U103

77-78-1

Sulfuric acid, dimethyl ester

ON2147

U210

127-18-4

Tetrachloroethylene

ON2166

U213

109-99-9

Tetrahydrofuran

ON2178

U216

7791-12-0

Thallium chloride TlCl

ON2234

U214

563-68-8

Thallium(I) acetate

ON2007

U215

6533-73-9

Thallium(I) carbonate

ON2095

U216

7791-12-0

Thallium(I) chloride